A ST U D Y OF THE WATER MO L D S OF THE LYDELL STATE F I S H H A T C H E R Y AT CQiSTOCK PARK, MIC HIG AN 4 I E DWIN Y. MON SM A A.B., Calvin College, 1925 S . , University of Illinois, 1927 A THESIS Submitte d to the Faculty of Mi ch igan State College in partial fulfillment of the requirements for the degree of Doctor of Philosophy, 1935. ProQuest Number: 10008390 All rights reserved INFORMATION TO ALL USERS The quality of this reproduction is dependent upon the quality of the copy submitted. In the unlikely event that the author did not send a complete manuscript and there are missing pages, these will be noted. Also, if material had to be removed, a note will indicate the deletion. uest ProQuest 10008390 Published by ProQuest LLC (2016). Copyright of the Dissertation is held by the Author. All rights reserved. This work is protected against unauthorized copying under Title 17, United States Code Microform Edition © ProQuest LLC. ProQuest LLC. 789 East Eisenhower Parkway P.O. Box 1346 Ann Arbor, Ml 4 8 1 0 6 - 1346 Outline I In troduction II Des cr ip tion of the Hatchery III Methods and Technique IV Relative Abundance of Water Molds in Sources, Ponds, and Soil V Classif icatio n and Descript ion of Isolated Molds VI Experiments to Determine the Extent of Water Molds VII Discussion of the Necessity and Possibility of Control VIII Summary IX Literature Cite d ofParasitism Introduction It is a matter of common knowledge among mycologists and ichthyologists that certain water molds are very prevalent in fish hatcheries* Fish and fish eggs are often attacke d by such molds which effect the destruction of countless numbers* It is u su ally assumed that at least one of the species of Saprolegnia, J3. parasitica Coker, is parasitic on fish and fish eggs. Alt houg h the degree of parasitism is difficult to determine, (10) has given some valuable Kanouse information on this subject in her paper on S.. parasitica published in 1932. Coker (4) in his monog raph on the Saprolegniaceae also refers to S. parasitica as being associated with yo ung fish and fish eggs especially in hatcheries, but he also reports the collecting of several other species from fish hat che ry ponds. Duri ng the summer of 1934, 252 samples of water were collected from 15 different sources, Michigan. chiefly from We st er n Eighteen samples of water were collected from ponds of the Lydell State Fish Hatchery at Comstock Park. 12.3$ of the samples from Weste rn Mic higan produced water molds on hemp seeds, whereas 55.5$ of the samples c o l le cted from the hatchery ponds yiel ded molds. This great difference could not escape the attention especially since it was evident that the molds from the fish hatche ry 2 were not all species* parasitica but represented various In a conver sation with Mr. Claude Lydell, manager of the hatchery, to whom the author is indebted for a great deal of assistance and information, he was informed that these troublesome fungi had increased considerably in the last few years, each year, and that great losses were suffered presumably due to the fungi. It was evident that a th oro ug h study of the water molds of the fish hatchery, the kinds of molds found, of water supply, especially with reference to their distribution, the sources and soil contamination would not only be interesting and instructive, but might eventually lead to some met hod of control. The writer is greatly indebted to Doctor E. A. Bessey, of Mi chig an State College, under whose direction this work was undertaken, for his helpful advice and encouragement; and to Doctor R a l p h Stob, president of Calvin College, who at all times showed a spirit of helpfulness in provi ding laboratory facilities. Descrip tio n of the Hatchery. The Lydall State Fish Hatchery is located in Comstock Park, two mile s north of Grand Rapids on Hi ghway 484. grounds cover an area of about 32 acres. On this tract 26 ponds of various sizes have been constructed. one of these pond s have soil bottoms. Mill Creek, supplies most of these ponds with water, the hatchery grounds. All but which winds through The h a t che ry proper receives its water from Strawberry Creek, The a tributary of Mill Creek. 3 St rawb er ry Creek runs into Mill Cr eek about three-quarters of a mile north of the hatcher y grounds. bee n built, one in Strawberry Creek near its mouth, other two in Mill Creek. and the The accompanying map indicates the p o s i t i o n of these dams. From above each dam the water is piped to the various ponds. the map. Three dams have The pipes are indicated on Eac h pond receives an inlet pipe and has an overflow pipe wh ich becomes the inlet pipe for another pond. The ponds are thus connected in a series so that the water runs from one into another and then back into Mill Creek. ma y be several ponds in a series. with a drainage pipe which, There Each pond is also supplied when open, drains the pond and carries its water directly to Mill Creek. The ponds are drained in the fall and the spring of the year. The exact course of the waterflow through the ponds m a y be traced by following the arrows on the map. The numbers and letters given on the map correspond to the pond numbers used by the hatchery officials and employees. These numbers and letters will be used in naming the ponds in this paper. Methods and technique. In order to study the water mold contamination of this ha t c h e r y to the best advantage it was deemed advisable to make collections of both water and soil and to divide these collect ion s into the following ma in groups: 4 1* 2. 3. 4. Water from the sources. Water from the ponds. Soil from the bottom of the ponds. Soil from the hatchery ground in the pr o x i m i t y of the ponds. The water from the sources was collected from four locations as follows: Loc ati on A. Location B* Locatio n JS. Location D. Strawberry Mill Creek Strawberry Mill Creek Mill Creek Creek above Creek above above just above the dam. the point where joins it. the first dam. the second dam. For a more accurate und erstanding as to the positio n of these locations the map m a y be referred to. Te n collections were made from each of the four locations, is, that in all 40 collections from the sources. Five collections of water were made from each of the £6 ponds, mak in g 130 collections from the ponds. The soil collections from the bottoms of the ponds had to be taken when the ponds were drained. Since the water is drained out for only a short time the number of co llections was n ec essarily limited. The writer was able to get 4 soil collections from each of the 12 ponds, making 48 in all. In addition to this 19 collections were made from other ponds at random. For the sake of comparison 48 collections of soil from the h a t c he ry grounds were taken, that is, 4 collections near each of the 12 ponds from which the bottom soil was taken. For these collections a collecting belt with 18 screw top vials of about 20cc capacity was used. sterilized each time before taking them out. The vials were At the point 5 where the c ol le ction was made the entire vial was submerged and the screw top removed and replaced a few inches below the surface of the water. In this manner the po ssibility of co nta min ation with mold spores from other sources was eliminated. Soil collections were made surface in similar vials. The soil was removed at the point where the sample was taken and a soil boring was made with the vial no thing but the sterile vial touched the soil sothat that was collected. In the laboratory, both soil and water samples were transferred to sterile Soyka dishes. To the soil sterile distilled water was added and the two were mixed by agitating the dish. Into the Soyka dishes a couple of sterile hemp seeds and a sterile house fly, sterilized in a pressure cooker under 15 pounds of pressure, were dropped. If, mold spores were present the hyphae would usually appear on the hemp seed or fly within one week after the co llectio n was made. To get these molds into pure culture, single hyphal tips were transferred to potato dextrose agar plates. This isolation of single hyphal tips was performed under a binocular dissecting microscope and by means of two specially constructed needles. The needles were made from the fine platinum wire of a discarded radio tube. A little piece of this wire can easily be fused into the end of an ordinary piece of glass tube, this making it easy to handle. G rowt h on the agar plates was evident very soon after the is olation of the hyphae. About two days later a piece of 6 the agar about Jem square and containing hyphal tips was cut from these plates and transferred to ho meopathic vials containing about lOcc of sterile distilled water* For each form isolated at least 4 of these vials were set up. Sterile hemp seeds were dropped into two of these vials, sterile Dermesti d larva into the third, fly into the fourth. a and a sterile house The glassware used for these experiments was sterilized in an electric drying oven and the culture m e d i a in a pressure cooker at 15 pounds of pressure. During warm weather these cultures were kept in an ice box. During cold weather they were kept in a window box which was specially constructed for this purpose. inside of the window. The box was placed One of the window panes was removed and replaced by galvanized metal which contained an opening for a pipe 4 j w in diameter and 14j"long. the pipe was connected with the box. The other end of A damper was placed in the pipe to shut out some of the cold air during very cold weather. The temperature in this box ranged from 10 to 20 degrees centigrade; the average temperature was about 15 degrees centigrade. In most cases the characteristics needed for the classificati on of these molds were obtained from these single hyphal cultures. In a few cases, however, single spore cultures were made to determine characteristics more accurately. The technique followed to isolate single spores ma y be considered as a modified form of the method described by Ka uf fman (11). The writer's method is here given somewhat 1. in detail: Wi th fine scissors clip a quantity of mycelium 7 which is producing zoospores from a culture one of the vials. in 2. Mount this bit of mycelium water on a slide. 3. Stir the mycelium in the drop of water by means of fine needles, so as to set free some of the zoospores that ma y be adhering to the mycelium. 4. Now, with the needles, remove the mycelium, being sure to remove all hyphae and hyphal segments. (In this way only zoospores will remain in the water on the slide.) 5. Invert the slide and place it with the drop downward on potato dextrose agar in a petri dish. (The pressure of the slide will spread the water between the slide and the agar and at the same time disseminate the zoospores.) 6. Leave the petri dish over night. 7. U p o n microscopic examination the next morning it will be found that ma ny of the zoospores have germinated on the agar. 8. Remove the slide and cut out a bit of agar containing only one germinating zoospore. 9. in a drop of sterile Place this in the center of another agar plate and in a few days the plate will be covered with mycelium originating from the single spore. If the initial culture and if sterile is relatively free from bacteria instruments are used, it was found that this process can be used without danger of contamination, and with con siderably more ease and less consumption of time than any other method that was tried. Of great aid in the study of the details of the developmental processes was the use of moist chamber cultures constructed as suggested by G-iltner (6). 8 Window box used for culturing water molds during cold weather / < The open box showing interior con str uc ti on and one of the two removable shelves with culture vials* X 9 Relative Abundance of Water molds in Sources, Ponds, and Soil. The degree of water mold contamination of the sources, ponds, and soil as indicated by the molds produced in specimens brought to the laboratory can best be represented by a series of tables and charts. TABLE I Showing number of water molds pro duced in specimens of surface water from sources. Number; o f . .Time of Percentage j Number Specimens Collection ; Producing Producing Collected Mold Mold Locatio n of Co ll ect io n ! B 10 10/5/341/2/35 I 1 7 70 10 10/5/34 1/2/35 j 7 70 1 C 10 10/5/341/2/35 ! | 6 60 D 10 10/26/3412/14/34 | | 8 80 28 Av. 70 ! Total 40 . t-- : ------------- i ; 10 A 100 B C D Location of sources .-.. 90 Percentage 80 of ;------ samples produc ing Chart I molds Showing graphically the percentage of water samples from the sources that were contaminated with water molds. 7 0 % of all samples c ont am inat ed The table and chart just given show the contami na ti on of surface water from the sources indicated since all the samples were neces sar ily t ak en from near the surface. Whereas, the water pipe d to the ponds, deeper layers, is taken from the a question with regard to the accuracy of the results tabul ated above might arise. In order to determine the contamination of the deeper wate r h a w th or n fruits were suspe nde d in the water in ord inary soap shakers such as are used in kitchens for washing dishes. These h a w t h o r n fruits were left in the water for from one • to two weeks and then examined for water molds. results The for this experiment are here tabulated: TABLE II Show ing the re sul ts for the experiment with h a w t h o r n fruits to determine the mo ld contamination of the deeper layers of water from the sources. ...... .. ----- ..---- --.<.- L o c a ti on No. of h a w ­ Time of thorn fruits Suspension suspended ] A 10 10/13/3410/20/34 j A 11 ! A f No. with water molds Percentage of fruits with water mo lds 6 60 10/20/34 11/2/34 11 100 8 11/2/34 11/16/34 5 68.5 D 8 10/13/34 10/20/34 3 37.5 D 8 10/20/3411/2/34 6 87.5 3 11/2/3411/16/34 2 66.6 34 A v . # 69 j t ....... . -f D Total 1■«—----- •• 48 j | 12 These results are s t r i ki ng ly similar to those obtaine d with the samples of surface water from locations A and D, the latter showing a cont am in at ion of 75$ whereas these results give an approximate c o n t a m i n a t i o n of 69$. The difference that is negligible. We conclude, therefore, the c o n t a m i n a t i o n of surface water and deeper water is approx im at el y the same. The next table and chart give the results obtained for the 130 samples of water co lle cte d from the 26 ponds. 13 TABLE III Sho w i n g number of molds prod uce d in specimens of water from the ponds* Pond No. ,No. of Collect ions •Time of Co l l e c t i o n From To tfo* P ro du c­ % Produc-| ing molds 1 ing molds 1 5 9/28/34 - 12/14/34 4 80. 2 5 8/14/34 - 1/2/35 3 60 3 5 9/28/34 - 12/29/34 4 80 5 8/14/34 - 1/2/35 2 40 5 5 8/14/34 - 12/29/34 2 40 6 5 8/14/34 - 12/29/34 5 100 8 5 9/28/34 - 12/29/34 2 40 9 5 9/28/34 - 12/29/34 2 40 10 5 9/28/34 - 12/29/34 3 60 11 5 9/28/34 - 12/29/34 3 60 | 12 5 9/28/34 - 12/29/34 2 40 j 13 5 12/8/34 - 12/29/34 3 60 | 14 5 12/8/34 - 12/29/34 5 100 | 17 5 12/14/34 -12/14/34 5 100 j 18 5 12/14/34 -12/14/34 2 40 19 5 10/26/34 -12/29/34 1 20 20 5 12/29/34 -12/29/34 1 20 22 5 10/26/34 - 1/2/35 0 0 23 5 10/26/34 - 1/2/35 0 0 25 5 10/26/34 - 1/2/35 4 80 24 5 3 60 Island 5 9/28/34 - 12/29/34 1 20 Cement 5 8/14/34 - 12/1/34 2 40 B 5 8/14/34 - 12/1/34 4 80 D 5 8/14/34 - 1/2/34 5 100 X 5 8/14/34 - 1/2/35 3 60 !. 4 Total ! 130 1/2/35 - 1/2/35 71 Av*«£ F14.A ! j About 54*6^ of all samples contaminated Showing graphically the percentage of water samples from the ponds that were contaminated with water molds 14 15 Table IV and Chart III show the results obt ai ne d for the 48 soil collections from the bottom of 12 ponds. About 4 0 ^ of these collections pr od uc ed water molds. Ninete en other soil collections from several different ponds but less than 4 from each pond are not included in this table and chart* The percentage of c o n t a m i n a t i o n was somewhat lower for these 19 samples. TABLE IV Showing number of water molds produ ce d in 49 samples of soil collected from the bottoms of 12 ponds* Number of No. of Time of collections No. pr o ­ % p r o ­ pond collections From To ducing ducing molds molds* 1 4 11/16/34-11/16/34 0 0 2 4 :11/23/34-11/23/34 1 25 3 4 11/9/34 -11/23/34 3 75 5 4 12/1/34 -12/1/34 0 1 6 4 11/16/34-11/16/34 3 | 75 9 -4 11/16/34-11/16/34 0 0 10 4 11/2/34 -12/1/34 ! 2 50 11 4 10/12/34-12/1/34 | 3 75 12 4 '11/9/34 -12/1/34 4 100 13 4 10/12/34-12/1/34 2 50 Island 4 11/16/34-11/16/34 1 25 Cement 4 11/23/34-11/23/34 0 0 Total 48 -- — ..-—... , -f. 19 Av 0 39.6 16 Soil was also collected from the ha tc he ry grounds in the pr o x i m i t y of the ponds listed in Table IV and Chart III* The results o b ta in ed for these soil samples are listed in Table V and Chart IV* TABLE V Showing number of water molds pro du ced in 48 specimens of soil col lected from the hatchery grounds* Pr oxim it y of Pond Wo. 1 2 4 3/22/35 0 0 3 4 3/22/35 0 0 5 4 3/26/35 0 0 6 4 3/26/35 0 0 9 4 i 4/5/35 1 25 10 4 | 4/10/35 1 25 4 | 4/10/35 1 25 2 50 j j 11 1 N o . of Time of Co l l e c t i o n No. produc- % pr o ­ Collections ducing ing molds molds 4 3/ 22/ 35/ 0 0 I 12 13, 15 1 \ | Island 4 4/5/35 4 4/10/35 1 25 \ 4 ! 4/5/35 0 0 4 | 3/22/35 1 25 7 A v.g £ 1 5 i j Cement 1 | Total ! i( 48 r | CHART III Showing results for 48 soil collections from the bottoms of 12 ponds Cem* I si. 11 11 i A b o u t 4 0 $ of samples contam inat ed with water molds CHART IV Sho wing results for 48 soil collections in proximity of 12 ponds Cem, Isl. O About 1 5 % of samples contaminated with water molds 18 A co m p a r i s o n of Tables IV and V and Charts III and IV indicates a striki ng difference betwe en the co nt am ina tion of soil samples from the bottom of the ponds and that of the soil from the fish h a tc hery grounds. It is evident that the r el a t i v e l y h i g h con ta mina ti on of the soil at the bottoms of the ponds can be traced to the water which is in the ponds for the greater part of the year. the dat a given above Further exami nat ion of indicates a uniform grad at io n of c on t a m i n a t i o n of the water from the sources to the water in the ponds and again from the water in the ponds to the soil from the bottom of the ponds. In the first the co ntam ina tion is 15$ higher th an in the second and in the second the co nt am in atio n is 15$ higher t h a n in the third. The results p r e s en te d in graphic form give a straight line curve: G r a p h rep rese nt in g the relative co ntamination of sources, water in ponds, and soil from bottom of ponds. 100— Pe rc ent ag e 908 of 70.. 60L 5C_ Contaminat ion 4C_ 3Q_ 2Q_ 1Q_ Q1 19 It is dou btf ul whether the li nearity of this curve has an y significance* however, The general d i r e ct io n of the curve is, indicative of the general trend of contamination. The h i g h per ce ntage of cont am in at ion of the water from sources is no doubt responsible for the lower but n e v e r t h e l e s s serious co ntamin ati on of the water and soil from the ponds. Since water from all the four sources mentioned above is h i g h l y contaminated and since 19 of the 26 ponds receive their water either directly or in directly from source C, an attem pt to correlate the conta mina tio n of water from the sources with the contamin at ion of water from the ponds fed by them would h a r d l y be of any value. Suffice it to point out here that whereas water from source C showed a c o n t a m i n a t i o n of 60$, the average contamin ati on of the 19 p on ds fed by it is 55^. Here again we have the slight drop in co nt amin at io n from source to ponds as indicated by the graph given above. C la ss if i c a t i o n and D e scrip ti on of Isolated Molds. A s stated in the secti on on methods and technique an attempt was made to get the 120 forms p ro duc ed in the various samples of water and soil into or single spore cultures. single hyp hal-tip Ninety-four were successfully iso lat ed and an attempt was made to classify them. E a c h form was cultur ed o n hemp seed, a De r m e s t i d larva, in distilled water. a house fly, and From these three cu ltu res the characteristics necessary for cla ssi ficati on were in most cases obtained. Eight forms could not be 20 c la s s i f i e d because of lack of information. Three of these forms were def initely S ap rolegnia but the species could not be determined. Three others were A c h l y a but the ch ara cteris tic s for species det ermination were lacking. The remainin g 79 forms were referre d to species by the use of the k e y s given by Coker (4) and Hu m p h r e y (8). In each case the descriptions gi v e n by Coker and Humphrey were care­ fu lly read and compared with the results obtained in the study of the form under consideration. The original d es cr ip tio ns of the species were th e n consulted. Alth ou gh in a few cases the writer*s form did not agree in all details wit h the descriptions give n for the species in which he p l a c e d it, these differences he believes were of no great significance, since they might have been due to differences in environmental conditions. been s ho wn by Klebs It has repeatedly and clearly (13), Kauff man (12), Pieters (15) and others that these fungi are very sensitive to environmental conditions, and show differences in growth and structure dependent u p o n differences in nutrient media, and other factors. temperature, Taki ng this into consideration, the writer believes that the differences referred to above were of such a nature that they did not warrant the establishment of any new species. Some of these differences will be m en t i o n e d later in con ne ction with the species concerned. The following is a list of the species found and the number of times each species occurred, detail ed account for each species: followed by a more 21 Name of species No, of times it occ urr ed S a pro le gn ia p a r a si tica 34 Saprole gn ia ferax 17 S a p r o legn ia diclina 4 S a p r o legn ia hypogyna 4 Sa p r o le gn ia anisospora 2 Sa pr ol eg nia asterophora 1 S a pr ol egni a delica 1 Sapr ole gnia mi x t a 1 A c h l y a oblongat a var globosa 4 Ac h l y a K l e bs iana 3 A c h l y a racemos a 3 A c hly a ameri cana 1 A c h l y a hy p o g y n a 1 A c h l y a sp. 4 (sterile) Sapr o l e g n i a par asitica Coker Growth abundant o n most media, abundant, clavate, es pe cia lly on a fly. Hyphae with gemmae Gemmae cylindrical, spherical or subspherical, often in long chains. Pr olif er at io n of new hyphae through old zoo sporangia common. Zo o s p o r a n g i a abundant in vig or ous ly growing mycelium, cylindrical, averaging 200x26p, Oog o n i a few, not occurring in all cultures; smooth, thin, and unpitted. Diameter of oogonia 40-114p, dark and subcentric, 1-2 0 their di ame ters 19-24p, zoospores 10.5-12,25p. their walls Ant her idia diclinous. mostl y 60-80p. Oospores us ually 6 - 8 in each oogonium, a few as large as 30p. 22 This species occ urred in the collections as f o l l o w s : Number in w r i t e r 's c o l l ec ti on Locatio n of C ol le ct ion 285 Water from Pond 11 335 Water from Mill Creek, Water from Pond 3 347 348 Date of Collect ion 9/28/34 Loc. C 10/26/34 11/2/34 Water from Pond 4 Wa t e r from Pond 5 11/2/34 11/2/34 350 351 379 Water from Pond 6 Water from Cement Pond 11/2/34 11/2/34 Soil ; f rom Pond 12 11/9/34 381 Water from Mill Creek, 389 Wa ter from Pond 8 11/16/34 403 Soil ; f rom iPond € 11/16/34 417 Soil ;from Pond 2 11/23/34 424 Water from Mill Creek, Loc, B 11/23/34 425 Water from Mill Creek, Loc. B 11/23/34 426 Soil ; f rom ;Pond 10 12/1/34 428 Soil : f rom Pond 10 12/1/34 435 Soil : f rom Pond 13, 437 W at er from Mill Creek, 447 Water from Pond 14, 16 12/8/34 452 Esyrt gtom Pond 11 12/8/34 453 Wate r from Pond 10 12/8/34 454 Water from Moll Creek, Loc. 456 Wate r from Mill Creek, Loc. C 462 Water from Pond 17 12/14/34 464 Water from Pond 17 12/14/34 466 Water from Pond 17 12/14/34 476 Water from Mill C r e e k , Loc. B. 12/14/34 479 Water from Pond 1 12/14/34 483 Water from Pond 12 12/29/34 485 Water from Pond 10 12/29/34 501 Water from Pond X 1/2/35 505 Water from Pond 24 1/2/35 506 Water from Pond 24 1/2/35 509 Water from Pond 25 1/2/35 349 Loc. D. 15 11/9/34 12/1/34 Loc. D C. 12/1/34 12/8/34 12/8/34 23 A glance at the foregoing list will convince one of the general prevalence of Saproleg ni a parasitica. This species was collected from all the sources except Location A, Strawbe rry Creek, and from all but 9 of the 26 ponds. It was found in soil as well as water and it appeared quite c o n si stent ly from September to January. Kanouse (1 0 ) in 1 9 3 2 for the first time definitely n o t e d the appearance in this species. and described the structure of oogonia At least 10 of the 34 forms listed above p r o d u c e d oogonia in the writer's cultures. Invariably, ho w e v e r only a few oogonia were found in any one culture. The structure of th e s e agreed on the whole with the d e s c r i p t i o n and illustrations of Kanouse. o b ser ve d had diclinous antheridia, smooth, and unpitted. subcentric. Kanouse The oogonia their walls were thin, The oospores were very dark and states that the diameter of the oo g o n i a is 6 5 -1 3 5 x 6 0 -7 5 p i, or 65-95^1. The oogonia here ob s e r v e d measured 4 0 -1 1 4 p ., mo st ly 6 0 -8 0 jli. The oospores also ranged larger than the 1 8 -2 2 p . indicated by Kanouse. Their me as ure ments ranged from 1 9 -2 4 p ., and a few e xc eption all y large ones were 28 and 30 p. in diameter. Notwi ths tandin g these differences, these forms are no doubt Saproleg nia parasitica since the rest of the d es cr ip tion and the observations of Kanouse agree perfectly on the oogonia of this species. In his key to the species of Saprolegnia Coker (4) remarks that S. parasitica probably belongs to the Ferax group. However, since the oogone walls of the species are 24 thin, and pits, if present, are not conspicuous, since the an th eri dia at least and in the m a i n are diclinous, this species would naturally fall in the D i clin a group. Wi th reference to an abundance of Saprolegnia parasitica at the fish ha tc he ry the following summary can be made: Of the seventeen identified forms yielded by water from the sources 8 or approximately 47# were S. p a r a s i t i c a . Of the 46 identified forms yielded by water from the ponds 20 or approxima tel y 43# were j3. p a r a s i t i c a . Of the 16 identified forms yielded by soil from the bottoms of the ponds 6 or approximately 4 9 # were S. parasitica. From these figures it is safe to conclude that from 4 0 - 5 0 # of all the molds found at the hat chery are S. p a r a s i t i c a . Sa pro leg ni a ferax (Gruith) Thuret M o d e ratel y stout hyphae producing a large number of o o g o n i a and re la tiv ely few gemmae and zoosporangia. zoo spo ra ng ia form in old ones. zoospores about 10y* in diameter. New Zoospores escape separately; Oo gon ia have thick walls with large conspicuous pits, pits 5.25-7:00ji in diameter. A n t h e r i d i a observe d in only a few cases and then appearing to be androgynous, arising from the oogonial stalk. of oogonia 2 4 - 1 1 5 . 5yi, mostly from 60-80)1. 1 - 20 in an oogonium, oospores 19-30p, mostly less tha n 10. Diameter Oospores centric, Diamet er of usua lly 28-24p often varying in size in same oogonium. This species ranks next to _S. parasitica so far as f r e q ue nc y of occurrence is concerned. times as shown in the following list: It occurred 17 25 Number i n w r i t e r ’s collection l o c a t i o n of Collection Date of C o l l ec ti on 250 Wa t e r from Pond 6 8/14/34 275 Wa ter from Island Pond 9/28/34 286 Water from Pond 11 290 W ater from Mill Creek, 313 Water from Pond 10 318 9/28/34 Loc. B 10/5/34 10/12/34 Soil from Pond 18 10/12/34 319 Wate r from Pond 2 10/26/34 352 Water from Pond D 11/2/34 385 Water from Str awberry 420 W at er from Mill Creek 460 Water from Strawberry 465 Water from Pond 17 12/14/34 470 Water from Pond 18 12/14/34 471 Wa t e r from Pond 18 12/14/34 472 Wat er from Pond B 12/14/34 474 Water from Po nd B 12/14/34 493 Creek A C Creek A Water from Island Pond 11/9/34 11/23/34 12/8/34 12/29/34 W i t h the aid of the ke ys and descriptions of Coker (4) and Hu mph re y (8) these forms were rather easily identified. The large number of oogonia and the relatively small number of gemmae were evident in nearly all cultures. Wi th a very few exceptions the measurements of the diameters of oogonia and oospores fell within the extremes given by Coker. An ex cep tional ly small oogonium appearing in a fish hatchery 26 culture h a d a diameter of 24^i; an excep ti ona lly large oogonium m e a s u r i n g 115.5^ was found, extremes as 37p. and 97p, Coker gives the and while Coker gives 14.8p as a m i ni mum for the diameter of oospores, in the cultures u nd er c o n s i d e r a t i o n an oospore me asu rin g 12.25}i was found. The diameter of the pits in the oogonial walls is given as from 4.5ja to 5.5pi. Several mea su red in these cultures were at least 7ji in diameter. deemed to be of sufficient These differences are not significance for the establis hme nt of a new species or variety. The pre po nde ra nc e of evidence places all of these 17 forms in the species S. ferax. The conclusion, therefore, is that about 2 1 * 5 % of the identified forms were £>. ferax. Saprolegnia di c1 ina Hum phre y G ro wt h rather abundant. as in Saprolegnia. t h i n walls, M a n y gemmae and oogonia. unpitted, oog o n i a diclinous. Proliferation of zoosporangia diameter 45-80p. Oogon ia with Ant her idia on all Oospores m ostly 22-26p, us ually 3 - 1 0 in an oogonium. This species was found four times: No. 304 in water from Pond D on 10/12/34 No. 372 in water from Mill Creek, Loc. C on 11/9/34 No. 373 in water from Pond 25 on 11/9/34 No. 486 in water from Pond 19 on 12/29/34 These forms were compared with the descriptions and illustrations of Humph re y (8) and Coker (4) and were found to agree with them. identity. There can be no doubt as to their 27 S a p r o l e g n i a hypo gy na Pringsheim. Hyphae with new sporangia proliferating through older ones. Zoospores 10-12ju in diameter. c on s p i c u o u s l y pitted. Pits 5-7/1. Many oogonia which are Most oogonia have a pro top lasmic pr o t r u s i o n growing up into them from below. In addition some have androgynous antheridia arising directly be low the oogonium. 21-26/1; 1 - 1 5 Diameter of oogonia 30-70/2, Oospores mo s t l y 3 - 8 in each oogonium. This species was found four times as follows: No. 249 in water from Pond 6 o n 8/14/34 No, 314 in water from Pond 9 on 10/12/34 No. 410 in soil from Pond 2 on 11/23/34 No. 504 in water from Pond 24 on 1/2/35 From ^ o k e r 's (4) description of this species it is evident that it is a species with great variation in form. Pringsheim (17) first described the species as a variety of S. It was recognized as a species by de Bary (2). ferax. M a u ri zio (14) describes^ at least 5 varieties. In Ame r i c a a form of the species has heretofore been found only by K a u f f m a n in Michigan. The writer has compared the forms listed above with the original illustrations and descriptions of Pringsheim and de Bary and feels certain that these forms belong to this species. Whether or not they are the same form as the one which K a u f f m a n has found in Michigan has not been determined. Sa pro leg ni a anisospora de Bary Dense m y c el iu m growing well on all media used. Hyphae of medium thickness producing zoosporangia whose diameters are 28 a little greater th an the hyph ae bearing them* r e a d i l y p r o l i f e r a t e d through old sporangia* zoospores in each zoosporangium. d is ti nc tly different New hyphae R e l a t i v e l y few There are at least two sizes of zoospores in this species. The smaller ones are from 12-14ju in diameter when encysted, the larger ones up to 17*5ja* Oo gon ia moder at el y abundant, 30-60^1 in diameter with thin un pit te d walls. diclinous, branching, Ant he ri di a oospores 1 - 7 in an oogonium, in diameter, mo s t l y 17-21^i, 17-30 p. centric but soon breaking down, some appea ri ng eccentric when old. This species was encountered twice, from Pond 14. No. The record shows; 444 No. 8 40 in water from Pond 14 on in wa t e r Considerable species. The from Pond 14 on 12/8/34 12/29/34 difficulty was experienced in placing this "durchwachsung" of the zoosporangia clearly showed this form oospores both times in water to be a species of Sapro le gn ia . The howev er appeared to be eccentric, which is not cha rac teristic for this genus. Single spore cultures were made by the met hod described in the section on technique* Later a tuft of mycelium originating from a single spore and growing on a Derme stid larva was mounted in a hanging drop. The fungus continued to grow in this drop for at least 48 hours so that a thorough study could be made of the development of zoosporangia and the discharge of zoospores. Ob s e r v a t i o n soon showed that at least two different sizes of zoospores were discharged from different zoosporangia, a characteristic found in £>. A ni s o s p o r a . On the day fol lowing 29 this obs e r v a t i o n oogo nia were diclinous antheridia. starting to form* These bore The oospores were present in these o og onia on the next day and these were centric. of hyphae, zoospores, oospores, Measurements antheridia and zoosporangia were ta ken and these coincided with those given by Coker for _S. a n i s o s p o r a , with the except ion that the encysted zoospores v a ri ed from 12.25-17. 5ji. few, most of the The smaller ones were spores were either 14 or 17.5p. A single spo rangium gave rise either to the larger or the smaller forms. The swimming spores, however, were about 12ji in their smallest diameter which is nearer to the measurements given by Coker (4) who states; "the smallest spores are about 8-9ji in diameter, others from 10.5-ll.5ji, the large ones from 13.7-14.8ji. " This plant agrees also with the descriptions of de Bary (3) who gives no measurements. The oospores obs erved in the original culture and which were apparently eccentric were de Bary (3). observations similar to those illustrated by These oospores are no doubt abnormal and our substantiate Coker's suggestion: ".... one is inclined to suspect that de Bary who rarely made a mistake, was in t h i s case wrong in thinking the normal eggs eccentric. His figures clearly show eccentric eggs, have been bre ak ing down? other S ap ro leg nia but may they not This seems the more likely as no has an eccentric eg g . ” In connection with the study of this species in the h a n g i n g drop some interesting facts may be recorded: Ob servat ion s on an immature zoosporangium were started at 4:30 P.M., Ma rch 28, 1935. At 8:00 P.M. ha d formed at the tip of the sporangium. knob had take n on an oval shape. a spherical knob At 9:30 P.M. this Zoo spores were not yet 30 starting to form in the zoosporangium. however, The next morning, at 9:30 the zoospores had been discharged and could be s e e n encysted a short zoosporangium* distance from the mouth of the These were 17. 5p in diameter. Because the discharge of zoospores had not actually been observed, observation* another immature At 11:00 A.M. sporangium was found for this zoosporangium appeared at the tip of a hypha 12.25p. in diameter. itself was 26.25xl40p. The sporangium Its protoplasm was dense and was separated from the lighter protoplasm of the hypha by a distinct wall. The sporangial protoplasm;, however, no signs of breaking up into zoospore P.M. initials. showed At 2:30 the zoospores had been formed and the characteristic knob had been produced at the apex of the zoosporangium. From 2:30 to 2:35 there was a squirming movement of zoospores wi t h i n the sporangium. At 2:35 the uppermost zoospore escaped fol lowed immediately by the others, At first the escape was very rapid, one at a time. slowing down as the escape of the final zoospore neared. All the 32 large zoospores ha d left the zoosporangium in less th an a minute and were swimming about independently in quick gyrating m o t i o n not far from the mouth of the sporangium. zoospores were all large, These oval-shaped and of equal size, each m eas ur in g about 12x21 p. A pair of long cilia could be se en at one end of many of these zoospores. At 2:45, / t e n minut es after the escape of the first zoospore, of them was found to have encysted. encystments were closely watched. timed: gyrations one After that several In one the process was stopped and the zoospore lay quivering 31 or v i b r at ing for 30 seconds, then both ends contracted and the zoospore rou nded up into a spherical mass. lasted 30 seconds, lasted one minute. This also so that the whole process of encystraent At 2:55, 20 minutes after the escape, all the zoospores h a d encysted. These encysted forms were 14;00p in diameter. The rate of growth of a hyphal tip was observed in this hang ing drop culture. ocula r micrometer. The microscope was equipped with an It was placed in such a position that a growing hy p h a lay lengthwise directly unde rneath the scale.. The amount of growth was then observed at intervals for a p erio d of one hour, after which the slide was accidentally m o v e d and the readings could not be continued. The reading s showed the following results: from 1:03 to 1:23 the hyph a increased 21:00 microns in length from 1:23 to 1:43 the hypha increased 19:25 microns in length from 1:43 to 2:03 the hyph a increased 12:25 microns in length. The total increase for the hour was therefore 52.5 microns. Since the hypha was about 15ji in diameter the increase in one hour was about 3j times the diameter of the hypha. S ap rolegn ia as terophora de Bary Hyphae with pr olif era tion of new hyphae through old sporangia. On hemp seed and fly numerous small oogonia m o s t l y with papillae, in an oogonium. some smooth. Oospores most ly one Diameter of oospores about 22ji. of oogon ia about 26u not including papillae. Diameter 32 ^his form was found only once: No. 431 in soil from Pond 12 on 12/1/34 The pr ol i f e r a t i o n of new hyphae through old zoosporangia and the oogonia with papillae, oospores, havi ng mostly one, seldom two places this form with £5. as tero pho ra. Measurements t a k e n agree with those given by de Bary (1) and Coker Saprolegnia delica (4). Coker Mycelium rather delicate with cylindrical sporangia, oogonia with thin walls, pits not conspicuous. All oo go ni a with delicate diclinous antheridia sometimes nearly surrounding oogonium. Oo sp or es centric, Oogonia 50-70p in diameter. mos tly 5 - 10 in an oogonium. Diameter of oospores mos tly 24-26ju. This form was collected once: No. 272 in water from Pond 1 on 9/29/34 Its oogonia with thin walls and inconspicuous pits h a v i n g delicate antheridia which are mostly diclinous places this form with _S. d e l i c a . > Number of oospores per oogonium, size of oogonia and oospores, and the general appearance of the plant all coincide with Coker's original de sc ri pt ion and illustrations. Saprole gni a m i x t a de Bary Hyphae with nu mer ous oogonia and few gemmae. walls thick and with conspicuous pits about Oogone in diameter. Ma n y of the oogonia have antheridia some apparently diclinous, chiefly terminals, of the oogonis 40-70^i. Oospores centric, a few intercalary. Diameter Number of oospores mostly 1 - 10. diameter 19-25p. 33 This form was collected once: No* 273 in water from Pond 3 on 9/28/34 Thi s form is very mu c h like S3. ferax listed above, but because of the ma ny oogonia with antheridia it must accor din g to keys and descriptions be classed as ^S. m i x t a . Me asur em en ts agree with those given for that species. Coker (4) calls attention to the similarity of _S. ferax and m i xt a . A c h l y a ob lo ngata var globosa Humphrey Mycelium consis ting of long, num er ous zoosporangia. older ones. New zoosporangia produced below Zoo spores encyst at mouth of zoosporangium. En c y s t e d zoospores 12-15 p.. spherical, Oogonia abundant, most ly 50-90^1 in diameter, on nearly all oogonia, 6 - 2 0 stout hyphae with a few larger. diclinous. Oospores numerous, mos tly 12 - 15 in an oogonium, ap pa ren tl y subcentric, Antheridia centric, a few diameter 22-27pi. This form was collected under four numbers: No. 271 in water from Pond 1 on 9/28/34 No. 282 in water from Mill Creek, No. 434 in soil from Pond 13 on 12/1/34 No. 500 in water from Pond D on 1/2/35 Loc. D 11/9/34 The identity of this species cannot very well be mistaken. Since the oogonia were nearly all spherical oospores averaged more than 10 in an oogonium, and these forms are no doubt of the variety g l o b o s a , as indicated above, v ar iety esta blished by Hu m ph re y (8) on the basis of these ve ry characteristics. W h e n this form was first encountered (No. 271) the a 34 large and long hyphae were very conspicuous on hemp seed. These hyphae were exceptionally broad at the base and tap ered to a point at the top. One of the hyphae was found to be 27 1. 25p in diameter at the base. Wh en the hemp seed was h e l d out of the water the hyphae stood out straight 1*5 cm perpendicu lar to the surface of the seed. A c h i y a racemosa Short, di am et er Hildebr and slender hyphae with terminal zoosporangia of a slightly greater than that of hyphae. Zoospores encyst at m outh of zoosporangiuip, about 12/a in diameter. My c el iu m prod uci ng very many oogonia on short racemose stalks. The abundance of oogonia make the mycelium appear as a dense, white fringe aroung the substratum. 26.25-50.75/1, with thick, Oogonia smooth, yel lowish walls. oogonium bears one or two short, unbranched, a n t h er id ia which arise from the oogonial Each tuberous stalk directly beneath the oogonium. Oospores are 17.5-33.25/a averaging about 24/a in diameter, 1 - 3 sometimes 4 and very rar ely 5 in an oogonium. This species appeared three times: No. 330 in w a t e r from Pond 25 on 10/26/34 N o . 492 in water from Pond 20 on 12/29/34 No . 499 in water from Pond 4 on 1/2/35 This species stands out clearly from the other species A c h i y a because of its numerous oogonia on short racemose stalks, and by its short unbranched antheridia arising from the oogonial stalk directly below the oogonium. That all of the three forms belong to this species is evident since they possess all the characteristics up o n which H i l d e b r a n d (7) bas ed the species. Later it was described for Am e r i c a by Hum ph rey (8) and Coker (4). As to details of size in oogon ia and oospores and as to number of oospore in an oogonium all of these forms agree. however, Coker In this respect, the y differ somewhat from the forms described by (4) and Hu mph re y (8). small 40-70ji", Coker states "oogonia rather Thirty-two oogonia taken at random firom different cul tur es of our three forms showed that the oogonia var ie d from 26.25-50*75p. On the whole, therefore, th ey are cons ide rably smaller than those described by Coker. Further, Coker (4) states that the oospores are "variable in size 16.6-27. centric, in diameter, most about 1 -8 in an oogonium, in most cases 2 - 5 , centric. H u m p h r e y (8) with reference to number and size of oospores states "1 - 10, 25ja. " commonly 1 - 6 , Hi ld eb r a n d species states, (7) in the original description of the "In den Oogonien haben sich mehrere 3 - 1 2 Be fr uch tu ng sk ugeln gebildet." oospores, their diameter averaging As to the size of the forty oospores picked at random from our cultures va ri ed from 17.50 to 33.25^1 with an average diameter of about 24^. The difference is more marked, however, respect to number of oospores per oogonium. with All of the three investigators cited above placed the oospore number hig her than was found to be the case in any of these cultures. The oospores in one hundred oogonia in a my celi um growing on a Dermestid larva were counted. This appeare d to be a representative culture so far as this 36 point is concerned. 21 37 36 5 1 The result was as follows: oogonia contai ned 1 oospore oo g o n i a contained 2 oospores oogon ia contained 3 oospores oo gon ia contained 4 oospores oogoni um contained 5 oospores For these forms, therefore, the oospore number is 1 - 3, sometimes 4 and very seldom 5. At no time was an oogonium with more than 5 oospores observed. One might conclude from these data that a new and distinct variety of A* racemosa has been found. However, here again the differences recorded above m a y not be essential but may possibly be due to a nutritive factor. We again refer to the work of Pieters (15) on the vegetative vigor and reprod uctio n in S a pr ol eg niace ae . Special reference is made to his Table V (p. 544) where size and number of oogonia, and number of oospores in an oogonium are shown to vary with different percentages of peptone in the medium. Achlya Kl e b s i a n a Pieters Mycelium consisting of moderately stout hyphae. hyphae just New and zoosporangia branching off from older hyphae below a zoosporangium. diameter, about 12p in encysting at mouth of zoosporangium. walls unpitted. 63-10lji. Zoospores, Antheridia diclinous. Oospores eccentric, 17.5-24.5^1. Oogonial Diameter of oogonia 3 - 15 in oogonium, diameter ^ A. Kl e b s i a n a was collected on three occasions; No. 290 in water from Mill Creek Loc. B. on 10/5/34 No. 334 in water from Mill Creek Loc. C on No. 429 in soil from Pond 11 on 10/26/34 12/1/34 37 Thi s Piet ers Coker species was first described from Mic hi gan by (16). It is no doubt a truly M i chiga n species. (4) has, however, found it in North Caroli na in 1921. The forms listed above agree with the descriptions given by Pi e t e r s and Coker in the essential characteristics, di clinous antheridia, oospores. u n p it te d oogonial walls, These forms seem to differ, such as and eccentric however, from the p r e v i o u s l y described forms in size of oogonia and number of oospores per oogonium. the Pieters does not give the size of oogonia but in C o k e r ’s form they are usually from 48-62^1. In these forms they vary from 63-lOlp,. Pieters gives 1 - 10 as the number of oospores per oogonium. states 1 - 8 usuall y 6. oospores in an oogonium, number of oospores Coker In our forms there were from 3 - 1 5 averaging 9. The larger average is perhaps due to the larger size of the oogonia since the average oospore size is the same as that given by Coker. Notwithstanding the differences given above there can be no doubt as to the identity of the species. Ac h i y a ame ricana Humphrey Long tapering hyphae bearing oogonia having eccentric oospores. Walls of oogonia smooth, hyaline, and pitted. A n t h er id ia androgynous arising from the ma i n hypha near the oogonial stalk. 7 - 15 in oogonium, Diameter of oogonia 70-90p. Oospores 22-26p in diameter. Collected as: No. 422 in water from Strawberry Creek, Loc. A on 11/23/34 38 This species has not been reported from M i c h i g a n before. Since this form agrees wit h the descri pti ons and il lustr ati ons of both H u mphre y (8) and Coker (4) there can be no doubt as to its identity, Achlya hypogyna Coker and P e m b e r t o n A c h l y a wit h o o g o n i a of various papillae. shapes, Di a me te r of oog onia m o s t l y 50-80}i, 26-30}i, m o s t l y 28p, 1 - 13 in an oogonium. m a n y with oospores Antheridia androgynous. C o l le cted as No. 432 in soil from Pond 12 o n 12/1/34 Except for the number of oospores in an oogonium which is given by Coker as 1 - 7 us ually 3 - 5 , this form agrees entirely wit h descriptions and illustrations given for A. hypogyna. In the oogones found in this culture there are from 1 - 1 3 oospores, the average number being 5. It must without doubt be assigned to this species. Achlya s p . In his monogra ph on the Saprolegniaceae Coker (4) describes and illustrates an Ach ly a species which remained sexually sterile for several months and in which one could not induce the formation of oogo nia by means of culture m e d i a of various compositions. Among our collections were found four forms which agree with the description and illustrations of Coker. They were cultured for from three to four months without producing any sexual organs under conditions in w hi ch the other A ch lya species produced abundant oogonia. We have come to the con clusion that this 39 is most likely the by Coker* same A c hl ya species as the one referred It occurred in our collections as follows: No- 384 in soil from Pond 3 on cu ltured until 11/9/34 3/13/35 No. 391 in soil from Island Pond cultured until 11/16/34 3/16/35 No. 405 in soil from Pond 6 on cultured until 11/16/34 3/15/35 No. 416 in soil from P o n d 3 on cultured until 11/23/34 3/15/35 The accompanying chart shows graphically the relative abundance of the identified species described on the prece din g pages, from sources, ponds: as well as the relative number collected water from ponds, and soil from bottom of the UHART S H O W I N G RELATIV E ABU NDANCE OF DIF FE RE NT SPECIES (Based on the 79 species identified) i ft r a 1 i 1 d 0 1 i I cct o a i 1 0 0 0 0 d Q d o ft i •H 0 rH P 0 0 1—1 I P O 0 0 ft 0 -h X >» -H 0 d d 0 0 0 d r*»■rH rQ 0 £ rH 0 B 0 O XJ ftp d 0 o X* 0 4 3 0 x l P 0 Q rH d O bO 0 £2 d 0 d 43 0 0 0 •H d d •rH ft 0 0 0 X £3 XI 0 d O d 0 o 01 rH • 0 » O ••rH # ft o p • o • 0 • •pH • o • >> 0 • >> Is; 0 0 CQ aJ M «h CO CiDCQ O o CQ O CQ •H CQ £ CQ '©■!<2 0 < •H C d < 0 :-; 3S>3 4 3 2 1 y t4 *> ;w 41 In con side ri ng the distribution of any particular species with reference to sources, ponds, that this distri but ion is very general. pa r t i c u l a r ponds, and soil, That is, we find any species does not confine itself to sources, or soil. For instance, species are found in all three the most representative situations. Those that were en co un te red at least four times are likely to come from at least two locations. Seldom is a species found more than once or t w i c e at any particular location. From water from the .§>• A. f e r a x ,S * d i c l i n a , A. sources we obtained: _S. p a r a s i t i c a , oblongata var g l o b o s a , A. K l e b s i a n a , americana. From water from the ponds we collected; £!. p a r a s i t i c a , S. f e r a x ,_S. d i c l i n a , S. h y p o g y n a , S. a n i s o s p o r a , S. d e l i c a , £5. m i x t a ,A. oblon ga ta var g l o b o s a , A. r a c e m o s a , A. K l e b s i a n a . From soil from the bottom of the ponds we collected: S. p a r a s i t i c a , S. f e r a x , S. h y p o g y n a , S. a s t e r o p h o r a , A. h y p o g y n a , Ac h l y a sp. (sterile) T h i s general distribution of the species indicates a close c on necti on between the contamination of water in the sources, water in the ponds, and soil at the bottom of the ponds. Experiments to Determine the Extent of Parasi tism of Water Molds. Because of the abundance of these various mold species at the fish hatchery, reference the problem of their parasitism with to fish and fish eggs becomes important. Kanouse (9) 42 has con sidere d this problem with reference to _S. parasitica Coker. U p o n the basis of her experiments and observations she concludes that the means of zoospores infection of living eggs and fry by is not likely, but "that the pressure of growing hyphae on the egg membranes when the eggs are held tightly together is sufficient to allow pe netrat ion of the my c el iu m into the living eggs." (p. 449) Huxley (8) more or less assumed the parasitism of a form of fungus which no doubt was _S. parasitica Coker, upon the basis of the numerous infections of living fish in B r it is h rivers. It was deemed advisable, in connection with this problem to determine more definitely the probable parasitism of £>• par asitica and other species found in these collections from the hatchery. Accordingly the following experiments were undertaken. 1. Experiment with wall-eyed pike eggs. Living eggs of the wall-eyed pike, Stizostedion v i t r e u m , were obtain ed from a shipment received at the hatchery on April 20, 1935. Four apparently living eggs were placed in each of 63 vials, water. each containing lOcc of sterile distilled Into 7 of these vials Dermestid larvae on which the mycelium of £>. parasitica was growing, water with the eggs. were placed in the Seven other vials were infected similarly with S. f e r a x . Still others were infected with S>. d i c l i n a , S. anisospora, A. oblongata var globosa, and Achlya sp. 43 (sterile), se ven vials for each form. To determine whether the m y c e l i a thus pla ce d in the vials were actually pr od uc ing zoospores, sterile Dermestid larvae were placed in each of these 42 vials. and were mot larvae. These larvae floated on top of the water in contact with the mycelia growing on the other A n y subsequent infection of these sterile larvae must therefore be due to zoospores set free by the introduced mycelia. All the molds used were thus shown to be producing zoos por es in the water which contained the eggs. Ma ny of the eggs adhe red to the sides of the vials and with very few except ion s none of the eggs were at the outset of this experiment. were not in contact with the mycelium The remaining 21 vials infected and were used as controls. This was deemed nec es sa ry since as a matter of course the eggs could not be sterilized and some other check was needed in order to determine the likelihood of previous infections. All the vials were pl a c e d in an icebox where the temperature ranged from 10 to 15 degrees C . , mos tly 12 or 13 degrees. The first careful examination of these vials was made two days, or about 48 hours, after the experiment was started. From then on the vials were examined every day and the observations carefully recorded. The first examination showed that about 60# of the eggs in the cultures and about 50# of the eggs in the control vials were dead. The high mortality must be r e g ar ded as due to factors involved in the sudden changes to which these eggs were subjected whe n the experiment 44 was started. It is also possible that m a n y of the eggs were not f e r t i li ze d and con sequently died. cannot be ascribed to fungus infections This mortality since the m o r t a l i t y in the controls was nearly as high as that observed in the cultures. We conclude that only the eggs with the greatest vitality survived the sudden changes. These, therefore, were fit subjects for the object of this experiment. A further general statement may be made w it h reference to the first observations, namely, that none of the living eggs showed any signs of mold infections, whereas, 49# of the dead eggs in the cultures were definitely infected. None of the dead eggs in the controls were infected. ^he observations for each of the mold species were r e c o r d e d separately and can best be reproduced by a series of graphs. The graphs show the number of eggs that were dead and the number of eggs that were infected on each successive day. A curve for mortality and one for infection were draw n in each case. to the The proxi mity of the first curve second indicates how readily dead eggs are infected by the particular species of mold. at any point lies above, curve If the infection curve or to the right of, the mo rtality it indicates that living eggs were found infected. 45 Graph showing Mortality Curve and Infection Curve for S_» parasitica HI qJ cH 00 tO ^ lO O o h w to ^ 10 o ^ co o o h w to ^ ^ o ^ cp N o . OQ i— I i— | i— I rH i— 1 r—( i— ) i— I i— i rH CO CO CO CO CO 00 CO CO CO of eggs Q 1 a z 3 4 5 *T- 6 7 G r a p h showing Mortality Curve and Inf ection Curve for S>. ferax to. oHW«^ino^cooOHWto^ioo^«) r_ l ( \ ) f O ^ I O ^ o f ' C O ( J > H H H H H H H H H H ( M ( M W W W 0 3 0 J N ( J 3 N • Q 1 2 3 4 5 6 7 f PjTp-s §& 46 Graph showing Mortality Curve and Infection Curve for S. diclina ^ c o c n o rH H W t o ^ i o ^ ^ c o No. of eses CN2DO<^lOC0cr> HO HH WHi Ho ^H iH oHt o H H H W W W W O J e a W W W W to ^ LO tO SA'SQ • 1 2 3 4 5 6 7 G ra ph showing Mor ta lity Curve and Infection Curve for _S. anisospora 47 Graph Showing Mortality Curve and Infection Curve for A. oblongata var globosa 01 t>> ctf —| W IV U ) u ; C > UU o#HCvJto-«?i*int£>i>cocr»Or-ioo r i f— | 1— 1 r-1 r— I I— 1 I— 1 I — I rl H W W W W w w W W W No. of eggJ Gr a p h Showing Mo rt al it y Curve and Infe ct io n Curve for Achlya sp. OHNtO^lOONOaO^OHWlO^inONCO,, tO tO cOt>*00CT>pHr—I i—I i—I i—I i—I *—I rH i—I < —I OJ W CV} CXJ 0 3 CVj (X} (X? n f p n-o-q &o 48 A n ex a m i n a t i o n of the foregoing graphs brings to light c e r t a i n facts wh i c h are here summarized: 1. All of the species used in the experiment infect dead fish eggs nore or less readily* 2. S* par asi tica appears to infect dead fish eggs more readily th an do the other Species us e d in this experiment* 3. S. p ar asi tica is parasitic on fish egg s to a ce rt ai n extent. T ■‘‘his last statement requires further explanation and amplification* It was observed that in no case was a living ©Eg lying out of contact with the mycelium infected. Such an infection of dead eggs, however, was observed repeatedly i n cultures of all of these molds. It appears, therefore, that none of these molds are parasitic on fish eggs so far as infections by isolated zoospores are concerned. In a few cases living eggs were observed to lie in contact with growing mycelium. enw ra ppe d the eggs In those cases the hyphae so that they could not easily be dislodged from the meshes of the mycelium. These cases were studied ca refu ll y with the aid of dissecting and compound microscopes. The my celium was removed from these eggs in so far as this was possible without isolated and put injuring the egg. in a moist chamber. These eggs were then In this way subsequent development of the my cel ium on the egg membranes and of the eggs could be watched. manner. Five eggs were isolated in this Three of these were surrounded by hyphae of S. p a r a s i t i c a , one by hyphae of _S. d i c l i n a , and one by hyphae of A. oblon gata var globosa. In all cases the 49 hyphae a t t ac he d themselves to the egg membranes very firmly so that it was ha rd to remove them. seem to be due to any physical This phenom eno n did not factor such as pressure since in all cases the eggs lay close to the mycelium but the hyphae were free to grow around them without becoming attached. Rather, positi ve tropism could hyphae this time the phe n o m e n o n appeared to be due to a in the nature of t h i gmotr op is m. In no case be observed penetrating the egg membranes at as was the case in the infected dead eggs. These iso la ted eggs were kept in the ice box with the other cultures. Five days after the isolation of the egg surrounded by the hyghae of A. oblongata var g l o b o s a , the egg was still alive and developing, The hyphae containing a living and active embryo. showed no further development. The observations on the egg surrounded by hyphae of • diclina coincided with those on A. oblongata var g l o b o s a . Three days after the isolation this egg was still alive c on ta in ing a living embryo and showing no infection. Of the three eggs isolated with hyphae of _S. parasitica one was dea d the following day and was severely infected, a tuft of new hyphae extending from the focus of infection. The other two eggs were still alive but foci of infection in each case. they showed distinct These eggs were dissected and the foci of infection carefully examined under the compou nd microscope. It was observed that at these foci of infection small rhizoid-like hyphae were clumped together on the surface of the egg and rhizoids also extended into the egg. A m o n g these clumps of hyphae several germinating 50 zoospores were also observed. tubes, however, The pe netra tio n of the germ could not be determined. It is due to these observations that in the graph for S. p a r a s i t i c a the infection curve is to the right of the m o r t al it y curve on the last day of these observations. These obs erv ations also would lead one to conclude that .S* p arasi ti ca is parasitic on fish eggs at least to some extent. This parasitism and due to some external anJactive parasitism. is not merely incidental or passive, force such as pressure, It is limited, however, but it is to this extent that living fish eggs do not appear to be readily infected by single zoospores of £>• parasitica, but that due to the abundant growth of the hyphae on the surface of the egg the resistance of the egg is broken down and an avenue of entrance for hyphae and perhaps also for germ tubes becomes establi shed. During the five week period of our observations the eggs in the controls showed no mold infection whatsoever. The mort al it y rate of the controls was also much lower than that of the cultures. At our first observation-two days after the start of the experiment 41 of the 86 control eggs were dead. Seven days after the start of the experiment 44 of the 86 eggs were dead. It may safely be concluded on the basis of these observations that the eggs used for this experiment were not previously infected. The greater rate of m o r t a l i t y in the cultures may be due to the fact that these cultures had actively growing mycelia in them. of course, This, diminished the relative amount of free oxygen in 51 the culture water. It is possible, therefore that these culture eggs died for lack of oxygen rather than because of any direct effect of the fungi. This conclusion is substa n t i a t e d by our observations on one of the seven vials contai ni ng _S. d i c l i n a . The vial contained a very weak growth of this fungus as indicated by the shight growth of mycelium. All the eggs in this vial remained alive during the day pe r i o d of observation. the water was indicated, test larva on the 2. seven That zoospores were present in however, by the infection of the surface of the water. Exper ime nts with eggs of black bass. In the preceding experiment no difficulty was encountered so far as mold contamination of the experimental eggs was concerned. This was found to be an exceptional condition and yet one which is quite necessary in order to determine with any degree of certainty the parasitism of a particular species of mold. ne c e s s a r i l y ruled out. All methods of sterilization are The experimental eggs used in this experiment were taken from a nest found in Pon d 2 at the hatchery. Th e y were brought into the laboratory in water with a considerable amount of debris and also with eggs that were already infected with water mold. This mold was very e v i de nt ly a species of Saprolegnia and most likely _S. parasit i c a . From the material brought into the laboratory 250 eggs were carefully selected. out one by one, were alive, any mold contamination. These eggs were picked and were apparently free from Twenty-five of the eggs were placed 52 in each of 10 petri dishes con taining water from Strawberry Cr eek which had pr ev io usly been sterilized, a e rat ed by agitation. The eggs were cooled and spaced so that no two eggs were in contact with each other. Hemp seeds with wate r m ol ds growing on them were placed in 8 of these 10 pe tri dishes. E a c h of the 8 dishes was thus infected with a diff ere nt species of mold* The remaining 2 dishes were not inf ec ted and were used as controls. day, however, On the following the eggs in the control dishes were as badly infected as those in the other dishes. This showed d e f i n i t e l y that alt houg h apparently free from mold infection, the selected eggs were not actually free from contamination. The experiment as set up could not give any information in reg ard to the par asitis m of any particular species of mold. However, it could still throw light on the general “Does any mold zoospore, regardless of species, infect living fish eggs?" question, actually Here were 250 living eggs of the small-mo ut he d black bass, Micropterus dol om ie u, with no apparent mold infection, all carefully selected, in water from their natural habitat. and spaced Any infection that would subsequently take place must necessarily be due to zoospores set free in the water or to those that were o ri g i n a l l y clinging to the sticky surface of the egg membrane. These eggs were carefully watched to determine w he ther mold zoospores would infect living fish eggs. The results of the observations are recorded in the following* table• 53 TABLE VI Show ing the results on observations of 250 small-mouthed bass eggs sub je ct ed to the z>ospores of va rious water molds. *Date of N o . of o b s e r v a ­ living tio n eggs not infected No. of living eggs infected N o . of de ad eggs not infected No • of dead eggs infected Total No. of dead number larvae not infected 6/6/35 250 0 0 0 0 250 6/7/35 98 2 66 84 0 250 6/8/35 22 3 49 176 0 250 0 0 0 239 11 250 6 /I0/35 W h e t h e r in this table an egg was listed as dead or alive dep en ded ent ir el y upo n its tr ans parency to light from the substage lamp of the microscope. that It is considered likely some of the eggs recorded as dead and infected may have been alive, column. since all doubtful cases were placed in this The five eggs recorded in Column 2 contained embryos $hat were def initel y alive. examined. These eggs were mic ros copically It was found in each case that the infection had not pe netrat ed beyond the egg membrane. r e a d i l y be remov ed with fine needles. This membrane could The embryo was then set free app ar ent ly alive and not at all infected. of the dead and infected eggs were also examined. Several In these cases the egg membr ane s could not be removed because of the pe n e t r a t i o n of hyphae into the embryo. On June 15, 1935, a collection of eggs of the large­ m o u t h e d black bass, Micropte rus s a l m o i d e s , was brought into the lab ora tory from Lake No. 2, of M o r g a n ’s chain of lakes in n o r t h e r n Kent Co* ©oritaminated. This batch of eggs was also badly On l y 53 living and apparently non-infected eggs could be isolated* These were put into 4 petri-dishes carefu ll y spaced as in the preceding experiment ob se rva ti ons were made* The results were much as those the prec eding experiment. start of the experiment, infected, without 17 of the eggs were dead and 34 were apparently living and not infected, These and the embryos were One of these eggs was in an advanced stage of development; was beating, and 2 2 eggs were again carefully the me mbr an es were removed, infection* in Twenty-four hours after the eggs were alive and infected. examined, and the larva was fully formed, its heart and the blood could be seen circulating through the vessels. E l e v e n of the 53 eggs used in this experiment hatched. The larvae were observed for several days. died in a few days. were Most of them Five became infected after death. None infected while alive. From these experiments it appears that zoospores of at least cert ai n water molds settle upo n the sticky membranes of bass eggs and there germinate and penetrate the membrane. The living embryo is not penetrat ed but due to the thick meshe s of hyphae on the membrane the embryo eventually dies and is th en pene trate d by the hyphae. 3. Experiment with eggs of the bluegill. Whet her one or more species of water molds are capable of infecting living fish eggs was not determined in the f o r e g o i n g experiments. An attempt to determine this was made wi t h eggs of the bluegill, ta k e n from Lake No, Lepomis p a l l i d u s . These eggs were 2 of Morgan's chain on June 12, 1935, T h e y were taken to the laboratory and e x p e r im en ta tion was st art ed the same day. gravel and shells. The eggs were found in a bed of fine None of them showed any mold infection. Four hu nd re d eggs were separated out, several changes of sterile water. cleaned, The eggs were then isolated as in the previous experiments, 25 in a petri-dish, wi t h sterilized water from Strawberry Creek. ing 16 dishes, 2 were was he d in Of the resul t­ infected with zoospores of j3. parasitica by the metho d described Tor the experiment with the small-mo ut he d bass eggs. Similarly, wi th zoospores of S_. ferax, ob l o n g a t a var* gjLobosa, A. 2 dishes for each mold. dishes were infected S_. d i c l i n a , S. a n i s o s p o r a , Achlya a m e r i c a n a , and A. K l e b s i a n a , The remaining 2 dishes were not infected and were used as controls. Sterile hemp seeds were d r o p p e d into each petri-d ish to test the presence of zoospores. Although the eggs appeared to be entirely free from molds at the beginning of the experiment and although they were thoroughly washed, it was soon evident from the in fec tion of control eggs that water mo ld zoospores were carried over into the experiment experiment, definite therefore, by the eggs used. This again falls short in giving us information with respect to the parasitism of any partic u l a r species of mold. However, the results do give some valuable information as to the tendency of these species toward infecting the membranes of living fish eggs. The results are tabulated below. 56 TABLE VII S h o w i n g results for bluegill eggs exposed to zoospores of various water molds. Name of N u m b e r of infected eggs Four days after start Total mo ld 1 day 2 days 3 days of experiment species after after No. Eggs after No.eggs start start dead start eggs not inf. of exp. of exp. of exp inf. and ha t­ not ched inf. S. p a r ­ asit ica 14 19 20 22 26 2 50 S.ferax 20 22 23 23 25 2 50 S.diclina 11 S. anisospora 0 A.oblong­ ata v gl 1 A. americana 1 A* Klebsiana 3 18 20 20 22 8 50 13 17 17 30 3 50 6 11 11 31 8 50 12 18 18 29 3 50 14 19 24 26 0 50 2 12 13 27 10 50 Control 1 It will be noticed that the preceding table does not rec or d whether the infected eggs were dead or alive. in fo rm at ion was purposely omitted in the table. bluegill Since eggs are small it is difficult to determine whether an egg is dead or alive, light, This even with the use of transmitted es pecially when the egg membrane small p ar ticles of fore ign matter. certainty, however, is covered with There is reasonable that all or nearly all of the eggs found infected one day after the start of the experiment contained living embryos. Several of the infected egg membranes were removed and living embryos were found inside. One of the 14 eggs infected presumably by _S. parasitica hatched a few hours after the infection was observed. All of the infected 57 eggs were remov ed from the petri-dishes and placed in other dishes as soon as infecti on was observed. These eggs were kept under obs erva ti on for some time. cases except the one ment ioned above, infected In all the growth of the mold in cre as ed and the embryo was killed. Since after one day the controls were only lightly infected it is evident that the h e a v y infections found in the dishes inoculated with S_. p a r a s i t i c a , _S. f e r a x , and S. diclina were due to the zoospores of these species. In each case the test hemp seed was inf ected and the eggs were surrounded by active zoospores. This experiment leads to the conclusion that the outer me mbr anes of living fish eggs are readily infected by zoospores of ce rta in water mold species including £5. p ar as it ica and jS. ferax, the two species found in such large numbers in the water and soil of the fish hatchery. As a result of such an infection the egg dies, unless the embryo is in an adva nce d stage of development at the time of infection, in which case the egg will hatch, the larva e vi dently being unharmed. 4. Experiment with bluegill fry. In the p r e c e di ng experiments the parasitism of certain water molds on fish eggs has been definitely shown. que st ion to be considered is, "Are living fish fry suscepti ble to water mold infections?" to this question the very young bluegill the pr ec edin g experiment were used. dishes none of the Another To obtain an answer fry produced in While in the petri- living fry became infected though they were surrounded by an abundance of mold zoospores. In order 58 t>o get these fry into conditions for better observations they were transferred from the petri-dishes to vials s u p p l i e d with fresh, hemp sterile Str awberry Creek water, and seeds with zoospores producing molds of the same species as those u s e d in the preceding experiment. Most of the fry lived for a week or more under these conditions. None of the living fry were infected. The results of the ob se r v a t i o n s are here tabulated: TABLE VIII Sh owing the results of Experiment 4, in which bluegill fry were exposed to various kinds of m ol d zoospores. St ar te d June 20 Name pate o:" obsei~vatio n of 6/24 6/85 6/26/ 6/21 6/22 de ad de ad dead dead mold DEAD Ito ',ni i pi i ni i pi . i ni species S. p a r a ­ sitica 1 1 S. ferax S. diclina S. anispspora A. obi. v glob. A. araericana A. Klebsiana 1 6/29 dead i ni 9 1 Totals i ni 2 11 2 19 0 21 2 2 16 0 20 1 1 12 10 3 11 15 6 1 2 6/27 dead i ni 6 1 ■to 1 - infected 2 17 2 24 0 22 1 2 3 1 Controls 4 2 1 ni- not infected The results for this experiment 6 1 1 3 18 1 Totals 7 2 9 11 142 show that of the 153 bluegill fry exposed to zoospores of water molds none were infect ed while alive, when dead. and bnly 11 were found to be infected The dead fry were removed at each observation. Since so large a majo rity of the fry were found dead without in fection it can be assumed that the few which were found 59 in fect ed die d from reasons other than the mold infection. This experiment, therefore, leads to the conclusion that waiter mo l d s are not parasitic on fish fry. 5. Experiment with small-mouthed bass fry. A n oth er experiment to determine the parasitism of water m ol ds o n fish fry was conducted at the hatchery with fry of the small mo ut hed bass. Approxima te ly one hundred fry were put into each of eleven battery jars such as are us ed in the h a t c h e r y for the ha tch in g of eggs. of these At the bottom of eight jars zoospore producing molds were placed. species used were S. parasitica, £>. a n i s o s p o r a , A. pr od uc ing zoospores o n hemp seeds, S. f e r a x , £1. d i c l i n a , oblongata var g l o b o s a , A. A. K l e b s i a n a , and A. r a c e m o s a . Two small dead fish, They were growing and pieces of boiled fish. picked from the hatchery tanks and badly inf ect ed with mold, were placed in the ninth jar. The other £ jars were left as controls. wh ich © a m e a m e r ic an a, All of these molds were in the laboratory. dermestid larvae, The Hatchery water directly from Strawberry Creek was used for this experiment. This water was kept running through the jars as it is ordi na rily done when eggs are being hatched. The fry were, therefore, under conditions similar to those that obtained when they were hatched. One day after the start of the experiment all of the fry were alive. About wi th y e l lo wi sh spots. possible 10# of them, however, were covered These were at first thought to be foci of mo l d infection. On the following day the 60 number of fry ha ving such spots had increased but no mold g r o w t h was in evidence. these Up on microscopical examination spots proved to be the cysts of a protozoan parasite, _Ichthyophtherius multifilius , an infusorium rather abundant at fish hatcheries and causing a disease kn o w n to ha tc hery m e n as the ’'itch" • No mold growth was observed on the second day nor was there any dying off of the fry. The start of mol d growth was looked for especially at the points of p r o t o z o a n infection but no such growth appeared even unde r the microscope. for 2 more days. Similar observations obtained On the fifth day after the start of the experiment ma n y of the fry had died. All the dead specimens were removed and microscopically examined for m o l d infection. seventh days. alive. The same was done on the sixth and On the seventh day only 108 fry were still The experiment was terminated at this time and the living specimens were also microscopically examined for mold infections. The observations for the 3 days were as follows: Number Number Total Number Total of dead specimens infected of dead specimens not infected nu m b e r of dead specimens examined of living specimens examined and found not infected number of dead and living specimens examined 411 406 817 108 925 Infected dead specimens were found in all of the 11 jars during the 3 day period that dead fry were found. This indicates that m o l d zoospores were present in all of these jars and that the living fry were exposed to them. Since the control jars were shown to contain mold zoospores by the i nf ection of dead fry, this experiment does not serve to show parasitism for any particular 61 species of mold* However, since no living specimens were se en wit h infections in any of the jars, the conclusion' that none of the mo l d species use d in this experiment are par as itic on fry of the small mouthed bass is warranted* This conclusion is similar to that reached for the fry of bluegills in the precedin g experiment. 6. Experiment with Lake Mi ch ig an Shiners In order to determine the effects of water molds on older fish an experiment with Lake Michigan shiners was undertaken. These fish were chosen because of their convenient size and because they are extensively used at fish hat cherie s as food for larger fish. A battery of eleven jars was set up as in the preceding experiment. Into each of these jars 6 shiners were placed, three of which were injured on the side by means of a scalpel. Da i l y observations for molds were made. These observa ti on s were carried on over a period of nearly two weeks. The dead fish were removed as soon as they were found and notes with regard to infection or no n -i nf ec ti on were taken. period, At the close of this observation 6 of the 66 fish were still alive and showed no mold infection, 26 had died from the effects of molds, and 34 ha d died from other causes. Of the living fish one was an injured specimen. was taken from the jar supplied with £3. f e r a x . It The other 5 ha d not been injured and were taken as follows; 3 1 1 from the jar from the jar from the jar containing A. oblongata var globosa containing A. Klebsiana containing the infected fish. 62 Of the 34 that died from c a u s e s other than mol d infection 5 escaped from the top of the aquaria and were found on the floor. The other 27 e vi dently could not adjust themselves to the confines of aquaria as well as some of their mates. Ma n y of them, however, lived for nearly two weeks. Special importance is attached to those 26 that died from mold infections. In n earl y all cases the infection co uld be seen on the living fish one or two days before it died* rapid. Once the growt h got started its^ spread was very Not one of the fish lived more than two days after the in fe ct io n was first observed. In 16 of the 26 cases that died from mo ld the infection started at the point of injury o n the side. In the others the infection started either at the tail or in the gills and head region. is significant, This since it is well kno wn that fish are ea s i l y injured during transportation and handling, especially at the anterior and posterior ends. These injuries may be very small and not noticeable to casual observation. It is ve ry likely that not only on the intentionally injured specimens but also on the others the infection started at a point of injury. Some of the infected fish were examine d mi cr oscopi cal ly and the infection was in e ve ry case found to be superficial, the hyphae never p en et rat ing deeply into the body tissues. appears In fact, it that the mold establishes itself at the point of injury and from there spreads as a thick mat of m y c el ium over;,the rest of the body, the tissues. but not penetrating D e a d and infected fish, were found in all the jars u s e d in this experiment, controls as well as the others. This was as expected since in the preceding experiment the water from Strawbe rry Creek was shown to contain mo l d zoospores. do not The results of this experiment, therefore, indicate that any particular species of mold is the offender. If, however, we consider the rate of m o r t a l i t y due to water mo ld in the various jars it does point to the fact that £>. parasitica if not the only offender. ma y be the chief For this reason, the in fo rm at ion that has bearing on this point is here given. TABLE IX Showi ng the mortality rate of the fish that died from mold infections No. of spec­ imens dying from mol d In jar cont aining: Rate of mold No. of day on which this mortality mortality per day occurred S. p ar asit ic a 4 3 1 1/3 S. ferax 1 3 1/3 S. dicl ina 3 7 3/7 S. a ni sosp or a A. obl ong at a var gl obo sa 3 3 2 10 1/5 A. K l e b s i a n a 3 6 1/2 A. rac emosa 1 8 Inf. 1 6 1/6 fish 1 . .. 1 / 8 Cont rol No. 1 3 9 1/3 Control 2 4 12 1/3 No. 26 64 O n l y the jar containing _S. anisospora showed a m o r t a l i t y rate that was at all close to that of p a r a s i t i c a as indicated in the column to the right. Since S. anisospora was not found in abundance at the h a t c h e r y it is doubtful whether this species contributes towa rd infections found in the ponds. The foregoing experiments lead to the following conclusions: 1. One or more species of water molds readily infect the membranes of living fish eggs by means of zoospores as well as by their hyphae. Such an infection nearly always results in the death of the embryo and further penetra tio n of the hyphae. 2. None of the mold species used in these experiments are cajpable of infecting living fish fry. 3. S a pr ol eg nia parasitica and perhaps also other species of water molds, by means of their zoospores infect living fish at injured surfaces and continue to grow from that point until a large part of the body of the fish becomes covered with a mat of mycelium as a result of which the fish dies. D i s c u s s i o n of the Necessity and Possibility of Control. A t t e n t i o n has bee n called in this paper to the general prevalence of several species of water molds in the ponds of the Lydell State Fish Hatchery. It; has further been sh own that the zoospores of many of these molds infect dead fish eggs readily and that one or more species of water molds will infect the membranes of living fish eggs by means of their zoospores as well as by their hyphae. There is no doubt that the death of many 65 thousands of fish eggs in these ponds annually is at least in part due to the prevalence of these molds. is evident It that the elimination of water molds from chis and similar situations would be of great benefit to fi sh culture. The problem of control, however, It is not sufficient, is a difficult one. as is frequently suggested, the ponds free from dead fish and spawn, to keep and other organic debris on which these fungi thrive, so long as the water supply from the sources is highly contaminated with mo ld zoospores. The problem resolves itself into the p u ri fi cati on of the water from the sources and this makes it still more difficult. to keep the streams, It is out of the question which supply the ponds with water, free from the organic matter which supports the life of these P h y c o m y c e t e s . the water If, as is the case in this hatchery, is conveyed from the sources to the ponds by means of pipes, it would seem that the proper time to rid the water of these dangerous zoospores would be when it passes th rough the pipes. If at this stage the water were trea ted with copper sulphate, ce rtai nl y be eliminated. for two reasons: kills first, the zoospores would But this treatment is ruled out because the copper ion which the spores is also detrimental to the life of fish eggs and young fish, and secondly, because there is a continual flow of water through the pipes and the ponds so that thousands of gallons of water would have to be tr eated daily. It is doubtful whether the expense of 66 such an u n d e r t a k i n g would warrant its usefulness. If copper ions could be set free in the water at one point and ag ain isolated and taken out of the water at a point further do w n before it reaches the ponds, the zoospores might the killing of be effected and the problem solved. Whether this would be possible through some method of electroly sis or some chemical process is a question which requir es further experimentation and study. so l u t i o n of the problem lies, perhaps, of physics and chemistry and beyond the intentions of this paper. The along the lines scope and Until such a purification process has been devised the usual precautions to free the ponds from all organic matter supporting the life of fungi should strictly be adhered to. A periodic draining and cleaning of the ponds and the subsoil is at present the best method to keep the fungi under control. Summary 1. 130 samples of water from 26 ponds, of water from sources, 40 samples and 115 samples of soil were collected from the Lydell Fish Hatchery with the purpose of determin ing the water mo ld contamination of this hatchery. 2. A new me t h o d for obtaining single-zoospore cultures of water molds 3. is described. Fourtee n species of water molds were isolated from the water and soil samples. These were identified and described. 4. It is found the _S. parasitica Coker is more 67 abundant in this situation t h a n any other species, isolated from the samples. 5« were The streams which supply the ponds with water found to be hi g h l y contaminated with mold spores of various species, so that the contamination of the ponds and the soil of the hatchery could be traced to these sources. 6. Experiments to determine the extent of parasitism of _S. parasit ic a Coker and other molds were conducted with the result that certa in of these molds were found to infect membranes of living fish eggs. They were found not to be parasitic on the fry of fish. One or more of these molds were shown to infect older fish at injured points and to effect the death of such infected f i sh. 7. The necessity and possibility of water mold control at the hatchery is considered. LITERATURE CITED 1. Bary, A. 2. Bary, A, de 3. Bary, A. 4. Coker, 5. de de W. C. Einige neue Saprolegnieen. Jahrb. f. wiss. Bot. 2:169-192. Pis 19-21. 1860 Zu P r i n g s h e i m ’s neuen Beobachtungen iiber den Befruchtungact der Gattungen Achlya und Saprolegnia. Bot. Zeit. 41:48-54. 1883 Species der Saprolegnieen. Bot. Zeit. 46:597-645, Pis 9-10. 1888. The S a p r o l e g n i a c e a e , with notes on other water molds. 201 pp. 63 pis. Un iv ers it y of North Carolina Press, Chapel Hill, N.C. 1923. Coker, W. C. and Pemberton, J. D. A New Species of Achlya. Bot. Gaz. 45:194-196. figs 1-6. 1908. 68 6. Giltner, W. 7. Hildebrand, 8. Humphrey, 9. Huxley, Lab orat or y Manual in General M ic ro ­ biology, 472 pp. 72 figs. John Wiley & Sons, Inc. Ne w York. 1926. F. Myc ol og ische Beitrage I. Ueber einige neue Saprolegnieen. Jahrb. f. wiss. Bot. 6:249-269. Pis 15-16. 1867-68. J. E. The Saprolegniaceae of the United States with notes on other Species. Trans. Am. Phil. Soc. 17:63-148. Pis. 14-20. 1892, 1893. T. H. 10. Kanouse, B. B Saprolegnia in Rel atio n to Salmon Disease. Quart. Jour. Mic. Soc. 22:311. 1882. A Physiological and Morphological Study of Saprolegnia parasitica. Myco lo gi a 27:431-4-52. Pis 12 and 13. 1932. 11. Kauffman, C. H. A Contribution to the Physiology of the Saprolegniaceae with Special Reference to the Variations of the Sexual Organs. Annals of Botany 23: 362-387. 1908. 12. Kauffman, C. H. K l e b s * T h eo ry of the Control of Developmental Processes in Organisms, and its Application to Fungi. Proceedings of the International Congress of Plant Sciences 2:1603-1611. 1929* 13. Klebs, Zur Physiologie der Fortpflanzung einiger Pilze II. Jahrb. f. wiss. Bot. 33:513593. 1899. G. 14. Maurizio, A. Zur Entwickelungsgeschichte und Systematik der Saprolegnieen. Flora 79:109-158. Pis. 3-5. 1894. 15. Pieters, A. J. The Rel at ion between Vegetative Vigor and the Re pr oduction in some Saprolegniaceae. Am. Jour, of Bot. 2:529-576. Text fig. 1, 2. 1915. 16. Pieters, A. J. New Species of Achlya and of Saprolegnia. Bot. Gaz. 60:483-490. PI. 21. 1915. 17. Pringsheim, N. Weitere Nachtrage zur Morphologie und Systematik der Saprolegnieen. Jahrb, f. wiss. Bot. 9:191-234* Pis 17-22. 1873.