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Advanc. l.irnnol. 60. p. 361-368

Biology and Management of Coregonid Fishes - 2005

Evaluating the success of large-scale whlteflsh stock­

ing at Lake COl1stance

Reiner Eckrnann!', Michael Kugler

2

and Christian Ruhle

3

with 2 figures and 1 table

Abstract: Artificial incubation of whitefish eggs at Lake Constancc (L.e.) started in 1887/88. Today there are six hatcheries at Upper L.e. which all use refrigerated water to delay hatching. They stock around 350 million recently hatched and 3-5 million prcfcd whitefish larvae annually. Despite this long history of artificial incubation at L.e.. it remains unknown whether stocking indeed fulfils its aims. to dampen yearly yield fluctuations and/or to increase yields. We used a newly developed method to label the otoliths of whitefish embryos during incubation with Alizarin Red S (ARS) to evaluate the contribu­

tion of unfcd hatchery larvae to cohort size. In winter 2003. 600 L of whitefish eggs were treated with ARS and by early April around -10 million larvae were released. In autumn 200.3. the otolith- of agc-O whitefish sampled from the lake were examined. We found that 18 out of a total of 290 lish originated from the marking experiment. Since only 10o/r of stocked larvae had been marked. the contrihution or hatchery-reared lish to the cohort 200.3 was estimated as 62'7< with binomial confidence intervals of 42 and 7()'7<. II should, however. not be concluded that stocking IS necessary to maintain the current level of commercial yields. since it still remains unknown whether hatchery fish are added to the naturally recruited stock leading to stronger cohorts. or whether stocking only increases intraspecific competition without enhancing cohort size.

Introduction

Releasing hatchery-produced coregonids into natural water bodies is an old and widespread practice throughout their native distribution range. The first reports of coregonid larvae stocking date back e.g. to 1867 in Finland (SALOL\RVl 1992). to 1887 in Germany (ROscH 1993). and to 1868 in Canada and the U .5. (Touu 1986). Since hatching of both naturally and artificially reproduced larvae mostly occurred at times when temperature and food condition, were considered suboptimal for larval growth and hence survi vat. the notion became general-

Authors' addresses:

I Limnoloaical Institute. Univcrsirv of Konstanz. 78457 Konsianz. Gcrmunv.

2 Wildlife :lIld Fishery Administrat'ion of the Canton of SI. Gall. Duvidstr.

35.

90() I St. Gallen, Swuzer­

land.

, Former head of Wildlife and Fishery Administration of the Canton of St. Gall. Hauptsstr, l , 8716 Schmerikon. Switzerland

.'. Corresponding author. e-rnail: reincr.cekmann0•uni-konstanz.de

1612-166X/07/0060-0361 $ 2.00

© 2007 E. Schweizerbart'sche Verlagsbuchhandlung. D-70176 Stuttgart

First publ. in: Advances in Limnology 60 (2007), pp. 361-368

Konstanzer Online-Publikations-System (KOPS) URL: http://www.ub.uni-konstanz.de/kops/volltexte/2007/3970/

URN: http://nbn-resolving.de/urn:nbn:de:bsz:352-opus-39700

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'

,

I 362 R. Eckmann, M. Kugler and C. Ruhle

11' accepted that later stocking of larvae would favour their survival. To delay hatching accordingly. the use of cold or artificially cooled water became standard practice in many hatcheries where larvae arc released soon after hatching.

As another means to foster larval survival, prefeeding of larvae with zooplankton was adopted early in the 20 th century. The labour-intensive cropping of zooplankron during times when ambient concentrations were still low promoted studies on the rearing of coregonid lar­

vae based entirely on the use of formulated feeds (DABROWSKt et al. 19~4. BERCiOT et al.

\986. Lt'CZY:--ISKt et al. 1986. Rc)sCH 1995). Only at the end of the 20 th century did suitable feeds become available that allowed the large-scale rearing of coregonids without any sup­

plementation by natural food.

In addition to stocking larvae directly after hatching or after a few weeks of prefeeding, stocking of juveniles during summer or autumn of their first year of life became increasingly popular. The first attempts to rear coregonid juveniles in Finland date back to the beginning of the 20 Lh century (SALOlARYI 1986J. but it was not before the 2nd half of the century that large numbers of juveniles were successfully produced in different countries for stocking into inland and coastal waters. As with coregonid larvae. juveniles were reared on natural food at the beginning. but nowadays they can be reared to the yearling stage on a diet of formulated feeds alone.

From the beginning of coregonid stocking. fisheries scientists and managers were keen to assess the efficiency and eventually optirnize their particular stocking practices, The most straightforward approach has been taken by CHRISTIE ( 19(3) by stocking whitefish into the Bay of Quinte. Lake Ontario. every other year. As commercial catches did not follow the pat­

tern of stocking. he concluded that climatic conditions had a dominant influence on year­

class strength and subsequent yields, Several studies on the efficiency of coregonid stocking used statistical analyses (GERDEAUX & DEW/\ELE 1986. ECKMAI\N et al. 1988. LLsnLA et al.

1995. WOLOS ct al. 1995) but could at best provide evidence that stocking may intluence yields or year-class strength. Reliable quantitative estimates on the influence of stocking on the fishery were hardly ever obtained (hut cr. GFRDI::AtJX 20(4).

In the case of stocking juveniles. the situation is different. These fish can he marked in several ways (spray marking. CWT. burning the adipose fin) so that their fate after release and their contribution to the natural stock can he quantitatively assessed (MENC et al. 1986.

C1IAMPIGNElILLE & GERDEAl'X 1992. LESKEI.A et al. 2(04). Due to the generally good success of juvenile stocking. statistical evaluations were more successful and more reliable results were obtained compared to corcgonid larvae stocking program"

Thus. the ambiguities that still exist as to the efficiency of larval stocking could possibly he overcome by treating these fish in a way similar to juveniles, i.e. marking these fish and assessing their contribution to the fishery. Most marking techniques that have been used with juveniles are not applicable to larvae due to their size at stocking (10-20 mm), The most applicable. cost-effective and safe method to mark fish of this xize i, by chemical labelling of otoliths. Appropriate methods of labelling otoliths with fluorescent dyes had heen available for some time (DABRows"t & TSUKAMUTO 1986. TSlIKA1\!OTO 198~. RlIHLE & WI:\EC"t­

KUEHN 1992. BLOM et al. 1994, NAGAlA et al. 1995. ROJi\s-BELTRAf' et al. 1995. 199~). No test has. however. been reported so far on the use of chemical labelling in a large-scale core­

gonid larvae stocking program (but er. ECKM;\N"J et al. 1995l. A first attempt at Lake Con­

stance was made in the 1990, using tetracycline. But. since hatchery managers have declined to use tetracycline in large-scale studies. a different technique using Alizarin Red S ha, been

established recently (Ec"\I"""

incubation. thereby avoiding t\1, impossible under the hatchery , The aims of our stud) \\ ere hatchery dimensions and (Ii I t, success under field condition-

Materials and method!

The experiment was carried Olil March 200~. Lake Constance I ' .:

pogeni« eurrophicarion (cl'. 13\1 I ­

the end of the 20'h century (totaI 1'1 fish (COl"('goll/l.l {(/\,((I"('I/I.I (L.) I I' vests (ECKVIAN\ & Rosru 19l)~, bated on average 7000 L of \\lut,':

of 70'1r. approximately 350 null:

end of April. plus an additional Ih, We used a recirculation systcm ", incubate 200 L batehe, of egg' \ a con-taut flow of lahelling soluti' ond tank received the solution 1'1,' trolled by a !loal switch, rccircu'.:

ed at around I'C in this hatchcr.

during mcubation.

The labelling solution was 1'1','1'

insoluble complexes with Ca it'll' otolith surface). but this reaction reaction. the amount of dissolved ably to lower murking succe-,-. TI"

cooled to the desired temperature ofARS t Alizurin Red S monohvu pUl11pS for about one hour. With th, with hydrochloric acid (HCI 25' ' menI was started.

Since the volumeratio of \\ hile

I: 10(ECKMAN'J 20(3). 200 L 01 Cc

drained to about 10 L. and bctv Cl'

were in a developmental stage \\ h mordiu. The pumps were started ,L incubation. pH and temperature hours. water from the hatchery', ARS was washed out after SOl1h' cooled water 10 remove any eVCl1tL ed into the hatchery', standard ]11 water treatment plant. where llll' admissible since a test by the S\\

had shown that the respiration rat,' tion of 100 mg L I,

In total. 600 L of eggs were I.t samples of around 500 mL were When larvae had hatched. one hilt, compare survival and growth bet»

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Evaluating the success of large-scale whitefish stocking 363

established recently (ECKMANN 2(03). The otoliths of whitefish embryos are labelled during incubation, thereby avoiding the need to label hatched larvae en muxse. which is practically impossible under the hatchery conditions at Lake Con stance.

The aims of our study were (i) to scale-up the method of ARS labelling of embryos to hatchery dimensions and (ii) to test the feasibility of this approach of evaluating stocking success under field conditions.

Materials and methods

The experiment VV~b carried our at Lake Constancc in the hatchery at Rorschach, Switzerland. in March 2003. Lake Constancc is the second largest prcalpine lake in Europe. After a period of anthro pogcnic eutrophication (cf. B\lIERLIc & GAIcDKIc 1995) the lake returned to oligotrophic conditions by the end of the 20th century (total POl-P during spring turnover was 9 pg L I in 200-1-). European while­

fish iCorcgonu: !I/I'(l/'C{US (L.)) is the dominant fish species accounting for >SO'!r of commercial har­

vests (ECK\l;\N'\ & Roscn 1998). Six hatcheries with a total incubation volume of 12000 L have incu­

bared on average 7000 L of whitefish eggs during the last ten years. With an average hatching success of 70'!c. approximately 3S0 million recently-hatched larvae are stocked het« een mid-March and the end of April. plus an additional three to five million prefed larvae which arc stocked in early summer.

Wc used a recirculation system of two circular tank-. (ISOI) L each) and six LUg jars (60 L each) to incubate 200 L batches of eggs. An immersion pump PlOO L min') in one tank supplied the jars with a constant flow of labelling solution. Thc Ilow rate could be adjusted separately for each jar. The sec­

ond tank received the solution from all jars. and an immersion pump (ISOO L min'), which was con­

trolled by a float switch. rccirculatcd the solution back into the first tank. Since embryos are incubat­

ed at around 1°C in this hatchery. a cooling system maintained the temperature between 1 and SUC durinu incubation.

The lnbcllinu solution was prepared from de ionized lake water for the following reason. ARS form, insoluble complexe-, with Ca ion-, (the reaction that leads to the irreversible deposition of ARS on the otolith surface I. but this reaction will also occur in the solution. if Ca ions are present. Through thi-.

reaction. the amount of dissolved ARS may decrease by up to 90'1r (KOClIIIN 1997). leading most prob­

ably to lower marking success. The rccircularion system was filled with 2000 L of deionized water and cooled to the desired temperature. Tris buffer was added at 1 12 L 1 and the nccessar; amount (I g L 1 )

of ARS (Alizarin Red S monohydrate. Sigrna-Aldrich: wa-. -tirrcd in and dissolved by operating both pumps for about one hour. With the pumps still operating. pH was adjusted tP.1 value between Sand S.5 with hydrochloric acid (HCI25'/r. diluted at I: [0). When pH remained <table during one hour. the treat­

ment was started.

Since the volume ratio of whitefish eggs (xcn linj; volume: and labelling solution should not surpass I: 10 (ECK\lAt\N 2(03). 200 L of eggs were treated at once. Both pumps were switched off. the jars were drained to about 10 L. and between 30 and 35 L of whitefish eggs were poured into each jar. The eggs were in a developmental stage where the otolith nucleus had just started to form by fusion of the pri­

mordia. The pump, were started a~ain and the flow rate was adjusted for each jar. During the 24 hours incubation. pH and temperature were checked regularly and adjusted when necessary. After 20-22 hours. water from the hutchery« cold incubation system was slowly added to the <ystcm. so that the ARS wa» washed out after some hours. For one or two additional days, the eggs were flushed with cooled water 10 remove any eventually remaining ARS from the chorion. They were then reincorporat­

ed into the hatchery', standard incubation system. The ARS solution was drained 10 the local waste­

water treatment plant. where the concentration was estimated to be well below I Jll~ L 1 This was admissible since a test by the Swiss Federal Laboratories for Materials Testing and Research (EMPA) had shown that the respiration rate of activated slud~ewas not influenced by ARS . even at a concentra­

tion of [00 mg L I.

In total. 600 L of eggs were labelled in three batches of 200 L each. From each batch. several sub­

samples of around 500 ml. were incubated separately 10 assess marking mortality during incubation.

When larvae had hatched. one batch of each treatment and a control were further kept in the hatchery to compare survival and growth between labelled and control fish.

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I

364 R. Eckmann, M. Kugler and C. Huhle

Onc or two days after hatching, the larvae were widely distributed in the main basin of Upper Lake Constuncc (Fig. 1), in the same way as larvae are normally stocked by hatchery personnel. In late sum­

mer/autumn or 2003. young-of-the-year whitefish were sampled from the lake at four areas (Fig. I) with a pelagic beam trawl of 4x4 m opening. Sagittae andlapilli were prepared Irorn all fish sampled and embedded in epoxy resin. Lapilli were examined ill toto independently be two readers with all epi­

fluorescent microscope (Zciss filter set no. 487915. 546 nm excitation wavelengthl. When results were doubtful. sagiuae were ground close to the nucleus. polished, and examined as above.

Results

Labelling success was 100% in all three batches (27, 30 and 40 larvae examined per batch).

Mark quality was scored 3 (cf. ECKMANN 20(3), i.e. marks were shining brightly at 10(h magnification. Mortality losses from the time of labelling until hatching were similar in treat­

ment and control batches, amounting to around 147(. Thus, in early April 2003,40 million labelled whitefish eleutheroernbryos were stocked into Upper Lake Constance. As mass hat­

ching of unmarked embryos occurred around early April in all hatcheries at Upper Lake Con­

stance, the release time of labelled and unmarked larvae coincided well. Naturally spawned whitefish, however. hatch about two months earlier.

Trawl samples in autumn 2003 yielded large numbers of juvenile perch, commercial-sized whitefish, and 290 young-of-the-year whitefish. The latter were more abundant towards the north-eastern as compared to the south-western shore (Table I), which corresponds to the general pattern of whitefish distribution during both the growth season (ApPENZELLER 1998) and winter (ECKMANN 1995). In 18 fish, i.e. 6.2% of sampled fish, ARS marks were easily detected upon inspection of the lapi Ili (mark quality 3). Additional inspection of the sagittae confirmed this result. It was necessary to check the sagittae in only two fish to confirm the

Rorschach­

o

5 10km

Fig. 1. Release sites for ARS-labellcd whitefish in Upper Lake Constance (open circles: 26.106 larvae, filled circle: 14·1Oil larvae released in April 20(3). Ellipses indicate regions where trawl samples were taken in late summer/autumn 2003 (clockwise from top: Langenargen west, Langcnargcn cast, Arbon, Romanshorn). Dots: recapture sites of labelled whitefish (n=18).

Table I. Results of trawling youne during autumn 2003. For location

Region No. or

l.angenargcn west 2i Langen.irgcn cast 1­

Arhon Romanshorn

non-existence of an ARS mark labelled fish were found at the bution of labelled fish within tl length range of the entire samp in length. This conclusion is fu ity and growth of labelled and, Since only 10% of larvae tl:

late that around 627r of the yOl 9SClr binomial confidence intc spans from 42 to 799r, i.e. wit would fall into this range.

Discussion

ARS labelling of whitefish oto chery conditions. Since ernbry.

30

~20 c Q) ::::J

u.. ~ 10

3 4

Fig. 2. Length-frequency distribu stance in 2()(l.'. To account for gr blocks: August samples (slashed hatched hars). Labelled whitefish

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Evaluating the success of large-scale whitefish stocking 365

Table 1. Results of trawling young-of-the-year whitefish in the central basin or Upper Lake Constance during autumn 2003. For location of trawling regions. refer to Fi~. I.

Region No. of hauls Total no. of Whitefish/haul No. of whitefish per

whitefish labelled whitefish

Langenargen west 20 135 6.8 I 9..~

Langcnargen east 1--1- 123 8.8 12..~

Arbon 6 17 2.8 17.0

Rornanshorn 5 15 3.0

non-existence of an ARS mark. One labelled whitefish was found among 12 to 19 fish (no labelled fish were found at the trawling region near Rornanshorn), indicating random distri­

bution of labelled fish within the cohort (cf. Fig. I). The lengths of labelled fish fell into the length range of the entire sample (Fig. 2), indicating that ARS labelling did not affect growth in length. This conclusion is further supported by observations in the hatchery, where mortal­

ity and growth of labelled and control fish did not differ during three months.

Since only 10S of larvae that had been stocked in 2003 were ARS-Iabelled, we extrapo­

late that around 627< of the young-of-the-year whitefish in 2003 were of hatchery origin. The 9S7r binomial confidence interval for detecting 180 hatchery fish in a sample of 290 fish spans from 42 to 79'/c. i.e. with an error probability of So/c the contribution of hatchery fish would fall into this range.

Discussion

ARS labelling of whitefish otoliths during egg incubation is possible at large scale under hat­

chery conditions. Since embryos are labelled during egg incubation. holding capacity for lar­

30

r;-20 c Q)

~::J

LL 10

3 4 5 6 7 8 9 10 11 12 13 14 15

Total length (an)

Fig. 2. Length-frequency distributions of young-of-the-year whitefish trawled from Upper Lake Con­

stance in 2003. To account for growth in length during the sampling period. data are grouped in three blocks: August samples (slashed bars). September samples (open bars). November sample, (LTOSS­

hatched bars). Labelled whitefish are highlighted in black for all three periods.

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366 R. Eckmann, M. Kugler and C. Ruhle

vae is not a bottleneck so that any hatchery can use our procedure. Thus. a method is avail­

able for evaluating the success of the massive stocking of recently hatched coregonid larvae into large lakes. This provides the possibility for objectively comparing different stocking practices. e.g. incubation at a natural temperature regime. delayed hatching via cold incuba­

tion. or prefeeding of larvae. Evaluating these different practices in addition to the already well-studied stocking of juveniles would allow selecting the practice. which is most appro­

priate for a particular management goal.

The scaling-up from laboratory to hatchery dimensions required some adjustments of the technical procedures. Care had to be taken to dissolve all the ARS before the pH was finally adjusted. Undissolved ARS floating at the surface was repeatedly stirred into the solution.

whilc the strong currents caused by the immersion pumps prevented settling of the chemical.

When adjusting the pH. a certain rime-tag had to be allowed for the solution to get thorough­

ly mixed after the addition of hydrochloric acid. The use of deionized water effectively pre­

vented the precipitation of Ca-ARS complexes in the recirculation system. Since the concen­

tration of dissolved ARS was probably much higher under these conditions as compared to the earlier laboratory trials. a reduced amount of ARS might be sufficient for successful la­

belling. Alternatively. the ratio eggs.solution could be increased. Small-scale trials arc, there­

fore. recommended to find out how much ARS can be saved by preparing the labelling solu­

tion with deionized water.

Our first, unreplicated estimate of 62% hatchery origin of the 2003 young-of-the-year co­

hort does by no means prove that stocking supports or increases commercial yields. Firstly.

the confidence interval for this estimate is rather broad (42 ... 799,) and the test has not been replicated so far. Secondly and most importantly, even if the contribution of hatchery larvae to a cohort amounted to around 6Wk it would not follow that without any stocking the cohort would be smaller. This would only be true if recruitment to the young-of-the-year stage was entirely density-independent. To our knowledge. this has never been shown for coregonids.

Instead. it is reasonable to assume at least some density-dependence of survival during the first months of life. This has been suggested as a general principle of population regulation in fish (e.g. RorSClIILD 1986. HouDE 1987). and there is evidence for density-dependent processes in coregonids from Finnish lakes (SAu)JAINI 1992). where the magnitude of densi­

ty-dependence seems to increase during ontogeny. Under the scenario of strictly density­

dependent survival to the young-of-the-year stage. cohort size could remain largely un­

changed even by massive stocking. through replacement of naturally-reproduced fish by those originating trom the hatcheries, Alternatively, if the carrying capacity of the system was not fully used by naturally recruited fish. then stocked fish might contribute significant­

ly to year-class strength.

Further insight into, and a quantification of, the effects of larvae stocking on whitefish po­

pulation dynamics and finally on commercial yields. can only be obtained by assessing sur­

vival rates of larvae from both sources. These assessments should preferably be undertaken under conditions of different ratios between. and absolute amounts of. wild and hatchery lar­

vae. i.e. replicates of our experimental approach are absolutely necessary. The notion that is recently becoming popular at Lake Con stance. that our first result already demonstrates the effectiveness of large-scale stocking of larvae into Lake Con stance must. therefore. be reject­

ed.

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edure. Thus. a method is avail­

'cntly hatched coregonid larvae

\ comparing different stocking aycd hatching via cold incuba­

riccs in addition to the already practice. which is most appro­

quired some adjustments of the ARS before the pH was finally uedly stirred into the solution.

vented settling of the chemical.

or the solution to get thorough­

lcionized water effectively pre­

uion system. Since the concen­

lese conditions as compared to be sufficient for successful 1£1­

.d, Small-scale trials are. there­

ly preparing the labelling solu­

[he 2003 young-of-the-year co­

lses commercial yields. Firstly.

79 c/r ) and the test has not been contribution of hatchery larvae '\ ithout any stocking the cohort re young -of-the-year stage was

er been shown for coregonids.

endcnce of survival during the iplc of population regulation in .idcnce for density-dependent

where the magnitude of densi­

le scenario of strictly density­

si7e could remain largely un­

t naturally-reproduced fish by rrrying capacity of the system .h might contribute significant­

.uvae stocking on whitefish po­

, be obtained by assessing SLJr­

iould preferably be undertaken runts of. wild and hatchery lar­

y necessary. The notion that is 'csult already demonstrates the ance must. therefore. be reject-

Evaluating the success of large-scale whitefish stocking 367

Acknowledgements

Myriarn Schmid prepared the otoliths. Rudi Wascm helped during the lahelling experiment. the rearing of juveniles and trawl catches. and Erich Stauh assisted with the statistical evaluation. The study was financed by the International Commission for Fisheries at Lake Constance and partly supported by the collaborarive research ccnter SFB -1-5-1-. Littoral of Lake Constance.

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