Bulletin STATE OF ILLINOIS DEPARTMENT OF REGISTRATION AND EDUCATION DIVISION OF THE NATURAL HISTORY SURVEY STEPHEN A. FORBES. Chief Vol. XV. BULLETIN Article VII. Some Observations on the Oxygen Require- ments of Fishes in the lUinois River BY DAVID H. THOMPSON PRINTED BY AUTHORITY OF THE STATE OF ILLINOIS URBANA. ILLINOIS October. 1925 ERRATA Page 57, statistical headings: for Year 1920 read Year I'JIO; for Year W09 read Year HUG; in the ratio heading, for 1909 read 1920, and for 1920 read 1910. The entries in the Year columns should change places. Page 85, line 13 from bottom, for 87 read 86. Page 88, line 20, delete red. Page 115, line 6, over the column of figures read Acres. Page 136, line 5, for /J.T read 131. Page 145, First table, 4th column, for S5.9~ read 33.40; last column, for .052 read .0418. Second table, second column, for .2158 read .2004; 5th column, for .1131 read .0977; last column, for .0926 read .0772. Last table, second column, for .714 read .663 and for total read $4,710; 5th column, for .374 read .323 and for total read $2,201; the last column, for .307 read .256 and for total read $1,700. Page 146: First table, second column, for 8.02 read 7.45 and for total read 52.92; third column, for 3.45 read 2.88 and for total read 19.10; 4th column for 19.28 read 17.90 and for total read 127.18; last column, for 8.29 read 6.92 and for total read 46.35. Second table, for 43.02 read 38.66. Last table, for 8.0 read 6.7. Page 382. line 10 from bottom, for Plat ytlieinis read Plathcmis. Page 385, in list, the specific names of No.'s 33, 35, and 40 should end in ns instead of a. Pages 445 (line 4), 448 (line 4), 449 (line 23), 454 (line 8 from bottom), read Belostomklac for Belostomatidae. Page 457, line 21, for cornutus read cornuta. STATE OP ILLINOIS DEPARTMENT OF REGISTRATION AND EDUCATION A. M. Shei.tox. Director BOARD OF NATURAL RESOURCES AND CONSERVATION A. M. Shelton. Chairman Wlliam Tkelease, Biology John W. Alvord. Engineering John M. Coulter, Forestry Kexdric C. Babcock. Representing the Edson S. Bastin, Geology President of the I'nivrrsity of IIU- WiLi-iAj[ A. NoYES, Chemistry nois THE NATURAL HISTORY SURVEY DIVISION Stephen A. Poures. Chief •-'S^^^S^^ Scii.NKi'f & Barnes, Printers Springfield. III. 1925 Article VII. — Some Obscnrntions on the Oxygen Requiretnents of Fishes in the Illinois River. By David H. Thompson. Introduction The amount of oxygen dissolved in the water is one of the most im- portant factors hmiting the fish life of the Illinois River. Every year low dissolved oxygen concentrations over a large portion of the river profoundly affect the food, distribution, and even the existence of the fishes. In the conservation of the Illinois River fishery it becomes neces- sary to evaluate the oxj'gen requirements of the more common fishes. The Illinois Natural History Survey and the State Water Survey have for many years conducted a biological and chemical survey of the Illi- nois River. As a result, the general oxygen conditions are rather com- pletely known for the various parts of the river during the different sea- sons of the year, and the distribution of fishes is well enough understood to show the general relation to the range of oxygen concentrations. The present paper is the result of an attempt to determine more precisely the minimal oxygen requirements of the common fishes and some of the effects of low dissolved oxygen concentrations, especially in winter. Dr. R. E. Greenfield and Mr. A. L. Sotier, of the State Water Sur- vey, made a series of dissolved oxygen determinations on the river dur- ing the latter part of January, 1925. They reported that the fishes were crowding into the "spring holes" in Peoria Lake, evidently on account of unsuitable conditions in parts of the lake which were frozen over. The writer, accompanied part of the time by Mr. Sotier, spent the latter part of January and all of February gathering data on the fish life of the river and making dissolved oxygen determinations in places where fishes were being taken, where fishes were dying, and where fishes usually had been taken but were absent at the time on account of special conditions of the water. Much credit is due a number of fishermen for collateral infor- mation and for their co-operation in the field work. Some valuable determinations of dissolved oxygen in the channel were made by the State Water Survey on January 23 and 24 and on Feb- bruary (i and 7, 1925, which are published here for the first time. The General Relation of Ice and Dissolved Oxygen It is a common observation that fish often die in the winter under the ice. This has been noticed most often where the ice has completely covered the water for a considerable period. It is also commonly said by 424 fishermen, in certain places, that when a hole is cut in the ice the fish will come to the place "to get air" and are very easily taken. It seems quite clear that the reason fish die under ice or come to holes in the ice is because there is a deficiency of dissolved oxygen in the water. A layer of ice over a body of water very effectually prevents the interchange of gases between the water and the air. The ice itself does not decrease the amount of oxygen, but it stops the aeration of the water. The decrease in amount of dissolved oxygen is brought about by the oxi- dation of organic matter in the water. This organic matter does not oxidize directly, but it forms the food of the bacteria and of larger plank- ton—the immense numbers of minute plants and animals which utilize the oxygen in their life processes. As a result, the amount of dissolved oxygen that is removed from the water depends on the amount of organic matter present and on the rate at which this is consumed by aquatic organ- isms. The life processes of these plants and animals which consume the oxygen go on very slowly in water that is cold enough to be covered with ice. It would seem that for this reason those lakes and very sluggish streams which are frozen over early and thaw out late would sutler most from the lack of oxygen. However, due to their sluggishness the solid organic matter settles to the bottom and can not quickly reduce the dissolved oxygen content of the whole body of water. In the deeper lakes fish do not die under the ice, probably because of the relative scanti- ness of organic matter and the greater amount of dissolved oxygen in the deeper water. In most streams large amounts of organic matter are constantly being added by drainage from the land and by wastes from cities. The stirring action of the current is usually sufficient to keep much of the solid organic matter in suspension and thus it exposes all parts of the stream to loss of oxygen. Some streams are so swift that they do not freeze over completely, and enough open water i.> left to keep the dissolved oxygen content of the water high enough for the life of fishes. Recent Observations on the Relation of Ice and Dissolved Oxygen in the Illinois River The Illinois River is not often covered with ice long enough for the oxygen dissolved in the water to be reduced to a point where the fish show signs of distress. The river froze over in December, 1924, and did not thaw out until the first week in February, 1925. It was completely covered with ice except for small patches of open water where the cur- rent was swiftest, notably in Peoria Narrows and below all bridges. Fishermen say that this is the first lime the river has been frozen over for any considerable time since the winter of 1917-1918. Kofoid* states that during the winter of 1894-95 the river froze over the latter part of December and the ice did not go out until the last of February.. Thb • EuL in. state Lab. Nat. Hist., 6:176. 1901. 425 ice was present during a prolonged period of low water, and it was ac- companied by the almost complete disappearance of the plankton organ- isms and by the death of large numbers of fish. Although this occurred before the Chicago Drainage Canal was opened, it must be remembered that the Illinois River was even then a heavily polluted stream. At that time the volume of water carried was much smaller than at present and the rate of flow was slower. It seems probable that the river because of its slower current was more likely to freeze over then than now, but that this tendency was partially counteracted by greater changes in level which tended to break up the ice and keep the channel open. During January and February, 1925, dissolved oxygen determina- tions were made in the Illinois River and related waters between La Salle and Meredosia. Table I shows the results of these determinations to- gether with notes on ice conditions and temperature of the water. Since the river froze over before Christmas, it seems probable that when the field work was begun, January 2;5, dissolved oxygen concentration had reached its lowest point. Sami^les taken on January 23 and 21 showed about 1.7 parts per million of dissolved oxygen at Peoria Narrows, Pekin, and Havana, but those from Henry and La Salle showed about 6 parts per million. This is probably not because of better aeration up-stream but becau.se the initial charge of oxygen dissolved in the water that diluted the sewage had, on account of the low temperature, not yet been consumed. It is quite probable that at this time the very low oxygen prevailed from Peoria Narrows to the mouth of the river at Grafton. On I'ebruarv 2. oxygen concentrations as low as 0.4 part per million were found in Mud Lake, which is partly fed by river water. Records of bullheads dying in the traps and seines in Treadway Lake and Coleman Lake indicate tbat low dissolved oxygen concentrations prevailed also in those back- waters that are fed by the river. A sample taken in the middle of Quiver Lake showed 2.3 parts per million of dissolved oxygen. This compara- tively high figure is due to the highly oxygenated water coming out of Quiver Creek. On February 4 samples taken in Treadway Lake and Coleman Lake showed over 5 parts per million of dissolved oxygen. This high figure is brought about by the dilution of these lakes with Sanga- mon River water. By February 5, when the river channel was partly o])en, sam])les at Beardstown showed 3.3 and 3.7 parts per million of dis- solved oxygen in mid-channel with 4.6 and 4.1 near the east bank, due to the better water coming out of Sangamon River. On February 6 and 7 there was much open water, but the water temperature w-as still between 0° and 4° C. Samples taken at Henry and Chillicothe showed about 5 parts per million of dissolved oxygen, which is somewhat lower than the up-stream samples taken two weeks previously ; but the samples taken at Peoria Narrows and Pekin gave about 3 parts per million, almost twice the amount found on the earlier trip. The thawing continued until the channel was free of ice by February S. On February 10 at Browning the channel showed 5.8 parts per million of dissolved oxygen. The next day at Beardstown it was 6.6. 426 > 427 Dissolved oxygen parts per 428 =5 ^^'^ 2 K ^- B H p. 00 t-_ 00 tP LA irf LA ec^ CO CS T-( CS M (^ Lri -rr M C-- -mch mesh four-foot hoop-nets. It was noticed a number of times that carp and buffalo taken from oxygen-deficient water were very light in color and sluggish in their movements, while the same kinds of fishes taken from well- aerated water were quite darkly pigmented and very active when disturbed. Mention was made by fishermen, from time to time, at several points on the Illinois River, of the inferior value of certain fish be- cause they were "gassy"—their expression for a taste and smell of the flesh of the fish, like the smell of coal gas. Others have described it as like the taste of kerosene or of tar ; but to the writer it seems more than anything else like the smell of the putrifying mud on the bottom of the river, which is very like that of coal gas. This taste is often so pronounced as to make the fish very disagreeable as food. "Gassy" fish are definitely associated with periods of prolonged ice on the river, mortality in nets and traps, and other indications of a .scanty supply of dissolved oxygen. The species which most com- monly have this taste are carp, buffalo, channel cat, and bullheads, and these are the species which are most often found living in water with a low oxygen concentration. If these fishes are kept in well-aerated M'ater for a few days, they lose this "gassy" taste. During the winter, except when the river is frozen over, fishes do not suffer directly from lack of dissolved oxygen. From November to May, in open water, the rate of aeration exceeds the rate of oxygen consumption, so that there is usually a sufficiency of dissolved oxygen. In midsummer, down as far as Peoria and .sometimes below, except during high water, lack of dissolved oxygen excludes fishes from large feeding grounds and destroys large amounts of fish food. For example, Mr. Richardson observed a heavy mortality of snails in Peoria Lake in August, 1917. As increase in temiterature accelerates the life processes of fishes, lack of dissolved oxygen can not be endured in warm water as long as in cold. 432 y. T-K f Eh o a to -C A lU S tS« t, • o p. M o CO a^ "' - ja . a S m w cj " " ^ a 0) QJ O ^M O J- o Jf oi :=: a! .2 •a ^u 3 rt c 433 434 435 Summary op Table II Col- umn 436 Bureau of Fisheries. The factors entering into the increase of the fish yield were principally : (1) The introduction of the German carp. (2) The increase in fishing operations. (3) The increase in the area of the river due to the addition of water from Lake Michig^an. (4) The increase in the food supply resulting from the sewage. T.UJI.K 437 taken. Here the factors making for increased yield have been offset largely by reclamation of the bottomlands. The greatest change took place in the Peoria-Browning section, where there was a marked increase in fish yield up to 190S and an equally marked decrease after 1908. Here the reclamation of bottomlands, notably the Thompson's Lake district, took place several years later than in the lower section of the river. In the upper section (La Salle-Chillicothe), although considerably less land has been reclaimed, and the higher stage of the river has increased the area of water, the fish yield shown by the 1921 and 1922 figures is scarce- ly half its former value. This decrease has been brought about entirely by the conditions produced by an excess of sewage.. The most important effect of an excess of sewage is the reduction of dissolved oxygen to a point where fish life is excluded from immense areas of water.