REPORT ON TYI'IIOIl) Ftffl IN Till! DISTRICT OF COLl'JIBIA SUBMITTED BY THE Medical Society of the District of Columbia TO THE COMMITTEE ON THE DISTRICT OF COLUMBIA OF THE U. S. HOUSE OF REPRESENTATIVES, JUNE 14, 1894. COMMITTEE: S. C. BUSEY. C. H. A. KLEINSCHMIDT. WILLIAM W. JOHNS TON. G. WYTHE COOK. G. L. MAGRUDER. S. S. ADAMS. D. W. PRENTISS. WA HINGTON: PRINTING OFFICE. 1894. REPORT ON TYPHOID FEVER IN THE DISTRICT OF COLUMBIA SUBMITTED BY THE Medical Society of the District of Columbia I A Y TO THE COMMITTEE ON THE DISTRICT OF COLUMBIA OE THE U. S. HOUSE OE REPRESENTATIVES, JUNE 14, 1894. COMMITTEE: 8. C. BUSEY. C. H. A. KLEINSCHMIDT. WILLIAM W. JOHNSTON. G. WYTHE COOK. G. L. MAGRUDER. S. S. ADAMS. D. W. PRENTISS. WASHINGTON: GOVERNMENT PRINTING OFFICE. 1 8 9 4. TYPHOID FEYER IN THE DISTRICT OF COLUMRIA. [Report submitted to the Medical Society, June 6,1894.] The committee appointed by the Medical Society to report upon the subject of typhoid fever in the District of Columbia begs leave to make the following report: The consideration of this subject by the Society is justified and demanded by the very great prevalence of typhoid fever and by the large number of deaths, which gives Washington a most unenviable position among American cities. It is right that a disease which is known to be preventable, which lias been almost abolished in some of the capitals of Europe, should receive here, in the capital of this country, the closest study and atten- tion. If the causes of its persistence are known-if, above all, these causes can be removed-it is our part and duty to make the facts public and to arouse public attention to the necessity and urgency for action. Who is better fitted to speak authoritatively on this subject than the Medical Society of the District, whose members are in daily contact with the disease, and who have every opportunity to study the modes of its diffusion among our population The committe has endeavored to present, as briefly as possible, the data upon which an intelligent judgment can be formed. The magni- tude of the task of making a complete study of typhoid fever in all of its aspects must be apparent to all, and the committee must ask in- dulgence for the imperfection of the report in many of its details. Much could only be touched upon, much had to be omitted. The im- portance of the subject demands continued observation and study, and it is suggested that the work be continued from year to year in whatever way which may seem best to the society. The committee is indebted for much valuable assistance to the Dis- trict Commissioners and their assistants, who have all shown great in- terest in the work of the Society in this investigation. The accompanying report will consider- 1. The prevalence and mortality of typhoid fever in the District. 2. The relations of the dissemination of the disease to the- (a) Public water supply; (&) To the pollution of the soil with the leakage from privies, from defective sewers, and from the backing up of sewage from tidal move- ments; 4 TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. (c) To the drinking of well or pump water; (d) To contaminated milk and to other causes. 3. The difference in mortality in different areas of the city, with a view to discover the causes of the disease. 4. Conclusions based upon the foregoing data, as to what measures should be taken to diminish the spread of the disease. PREVALENCE AND MORTALITY OF TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. The following table gives the statistics of typhoid fever in the Dis- trict of Columbia from 1881 to 1893, the ratio of deaths -from all causes, and the total deaths, based upon the records of the health office of the District: Table I.-: ■Typhoid fever in the District of Columbia, 1881 to 1893, inclusive. Years. Population. Deaths from ty- phoid fever. Ratio of deaths from typhoid fe- ver to 1,000 deaths from all causes. Ratio of deaths from typhoid fe- ver to each 10,000 popu- lation. Total deaths. 1881 183,000 67 16.2 3.6 4,136 1882 653 120 26.2 6.3 4, 571 1883 191,980 92 21.4 4.8 4,286 1884 000 76 16.0 3.8 4, 814 1885 200, 000 124 25.0 6.2 4,998 1886 205, 000 125 27.2 6.2 4,674 1887 210,000 116 25.0 5.5 4, 685 1888 225,000 168 33.6 7.4 5, 040 1889 250, 000 170 33.3 6.8 5,152 1890 250, 000 208 37.7 8.3 5,564 1891 000 208 36.6 8.3 5, 720 1892 260, 000 ' 183 30.4 7.0 6, 098 1893 285, 000 186 28.6 6.5 6,452 From 1881 there has been an almost uninterrupted yearly increase of the death rate, the highest point being reached in 1890, with a ratio of 8.3 to 10,000 inhabitants. In 1891 the rate was 8.3; in 1892 it had dropped to 7, and in 1893 to 6.5. The lowest mortality, 3.6 and 3.8, was in 1881 and 1884. The past nine years show a greater number of deaths, representing a larger number of cases, than at any previous time. In the past two years the ratio has been less than in the pre- vious seven years. An exception should be made to the percentage of 1893, as given in Table I. It is based upon an assumed increase of 25,000 population in one year. This is not thought to be justified by the actual increase of previous years, and the percentage of 6.5 as the ratio of deaths in this year should be much higher, as high, certainly, as 1892, which is 7 to 10,000 population. The actual number of annual deaths has increased from 67 in 1881, to 208 in 1890 and 1891, both years reaching the same number. In 1892 there were 183 and in 1893 186 deaths. Chart I. ACTUAL NUMBER OF DEATHS AND COMPARATIVE DEATH-RATE FROM TYPHOID FEVER, MALARIAL DISEASES, TYPHO-MALARIAL FEVER, AND DIARRHCEAL DISEASES, FROM 1881 TO 1893. Typho-Malarial Fever, _____ Malarial Diseases, . Typho-Malarial Fever and Malarial Diseases Combined, Typhoid Fever. Diarrhoeal Diseases, .... TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. 5 Table II.-Deaths from typhoid fever in Washington from 1883 to 1892, inclusive. Years. White. Colored. Total number of deaths. Number of deaths to 10,000 popula- tion. Total number of deaths. Number of deaths to 10,000 popula- tion. 1883 49 3.8 43 6.5 1884 53 4.05 23 3.3 1885 83 6.3 41 5.9 1886 81 5.9 47 7.05 1887 72 5.1 44 6.2 1888 95 6.3 73 9.7 1889 96 5.6 74 9.2 1890 118 6.9 90 11.2 1891 129 7.7 79 9.9 1892 107 6.1 76 8.9 5.8 7.8 In Table n the ratio of deaths in the white and colored population is given, in the ten years from 1883 to 1893, inclusive. The whites had an average mortality of 5.8 and the blacks of 7.8 to 10,000 population. Here, as in the general mortality statistics, the high death rate is due largely to the greater fatality of typhoid fever among the colored race. Typho-malarial fever is not included in these tables. If deaths from this cause were added to those from typhoid fever, as they should be done, the percentage of fatal typhoid cases would be much higher than here given. The present drift of opinion is to abandon this term alto- gether, as it leads to continued confusion and error. That it is being abandoned may be inferred from the decrease in the death returns from this cause, pari passu, with increase in the returns of typhoid fever. (See Chart I.) Table III.-Deaths from typho-malarial fever and malarial fevers in the District of Columbia and in Baltimore from 1881 to 1893. Deaths from typho-mala- rial fever in District of Columbia. Deaths from tvpho-mala- rial fever in Baltimore. Mortality from mala- rial fevers in District of Columbia. Mortality from mala- rial fevers in Baltimore. 31 50 99 27 44 44 112 22 38 48 93 24 34 66 66 29 30 75 78 27 17 58 55 30 22 55 99 28 14 41 62 24 28 33 80 23 35 54 68 19 20 39 56 26 23 33 62 19 18 31 85 25 The mortality from malarial fevers, as seen in the above table, is still greater than seems possible; the progressive falling off in the number of fatal cases, as seen in Chart I, shows either that malarial diseases are on the decrease or that there is a change of opinion as to the nature of many cases of fever. 6 TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. In order to represent more clearly the extent and fatality of typhoid fever in this city, maps have been prepared, which accompany this report. Map I is compiled from the maps of the health office, and is made up of an aggregation of the fatal cases of typhoid fever occurring in residences in five years from 1888 to 1892, inclusive, and shows the number of deaths (in red dots) during that period. There were in the whole city 626 deaths in residences from this cause. The same map shows (in blue dots) the number of deaths from the malarial fevers, including the deaths from typho-malarial fever. The actual number of deaths from typho-malarial fever in the five years was 120, an annual average of 24. There were 243 deaths from malarial fevers in the same period in residences, an annual rate of 48. No one can believe that malarial fevers have any such mortality in the District, and we are forced to the conclusion that many of the fatal cases of malarial fever were cases of typhoid fever. In public institutions and in the county the fatal cases of malarial fever numbered 130 in the five years, making a total of 493 deaths from this cause. The map shows that there is a coincidence in locality of the deaths from typhoid fever, typho-malarial fever, and malarial fevers. Deaths in the public institutions, hospitals, and in the county are not represented on this map; there were 201 in the hospitals and 90 in the county. Map III shows the locality of deaths from diarrheal diseases. Here, too, the area of greatest mortality is the same as that of typhoid and the malarial fevers. Table IV gives a comparative statement of the mortality from typhoid fever here and in a few of the chief cities of this country and Europe. The average annual mortality in the District to 10,000 popu- lation was 6.2; in Philadelphia, 6.3; Chicago, 7.8; Boston, 4.1; Balti- more, 4.1; New York, 3.1; Paris, 6.1; Berlin, 2. Table IV.-Comparative statement of the number of deaths per 10,000 inhabitants from typhoid fever in the cities named, during the years 1881 to 1893, inclusive, and the general average therein. Years. District of Colum- bia. Boston. New York. Philadel- phia. Chicago. Balti- more. Berlin, Germany. Paris, France. 1881 3 6 5 2 4 8 7.4 5.7 4 7 fi 7 1882 6 3 5 1 4 7.7 4. 6 3 o. 1 1A Q 1883 4 8 4* 6 4 7 6 3 3. 4 3 Q A 1884 3 8 5 3 5 6 1 4 1 Q o. » 7 1885 6 2 3 8 6 4 7. 4 4 A 1886 6 2 3 4 6 3 6. 8 3. 8 1 6 4 2 1887 5.5 4.6 2.9 6.2 5 3.4 L3 6.1 1888 7.4 4.1 2.3 7.7 4.5 3.8 1.4 3.3 1889 6.8 4.1 2.5 7 4.1 4.5 1.3 4.4 1890 8.3 3.4 2.2 6.3 8.4 5.6 1.9 2.9 1891 8.3 3 3 16 3. 3 0 9 9 9 1892 7 2.9 2.2 4.9 10.3 4.2 1893 6.5 Average 6.2 4.1 6.31 7.81 4.19 2.08 6.14 Chart II. R TO EACH 10,000 INHABITANTS UN-SEWERED CITIES . 1-8-4 UNLESS OTHERWISE STATED . u o >0© Uz® (0 lQ< u Ez° "Id 0 0) < X (t •- id < > u < o THE NORRIS PETERS CO PMOTO-UTHO, WASHINGTON, D C- Typhoid fever in the district of Columbia. 7 Chart II, adapted from the valuable report of Erwin F. Smith, now of the Agricultural Department, on The Influence of Sewerage and Water Supply on the Death Rate in Cities, shows the comparative mortality in different cities of this country and Europe.' We will have occasion to refer to this chart later. CAUSES OF THE PREVALENCE OF TYPHOID FEVER. What interests us most is to trace the cause of the disease as it exists here, and in so doing it is assumed in this report that the question of its etiology is definitely settled, and that the conditions underlying its prevalence are (1) an impure water supply, (2) the imperfect drain- age of a polluted soil, (3) infected milk, (4) and other causes. 1. The water supply of our city and the District comes chiefly from two sources, the Potomac River and the wells which are scattered about the city and county. Washington, out of fifty of the largest cities, stands second in the list, with a per capita and per diem public supply of 177 gallons of water. Only Buffalo, with 196 gallons, is better supplied, while Phila- delphia has 111 gallons; Baltimore, 92; Boston, 89; and New York, 74. Much of our public water supply is used in Government buildings and in public fountains, and the per capita estimate is not a fair one. It is not possible to compare the extent of typhoid fever in cities with abundant water supply with those which have an imperfect supply, or none at all, for cities well supplied with water are at the same time furnished with a good sewerage system, and it is not possi- ble in most cities to separate these conditions so as to discover the influence of water supply alone. The example of Dantzic, however, shows that an abundant water supply alone does not diminish the death rate. This city was supplied with water in 1869 and sewered in 1872. No marked diminution in the death rate of typhoid fever occurred until after the introduction of the sewers. Washington, with a daily individual supply of 177 gallons, has an average annual mortality of 6.2, while New York, with 74 gallons per capita, has 3.1 deaths yearly to 10,000 population. Abundance of water alone, as might well be supposed, does not limit the spread of typhoid fever. There is evidence enough to show that the public water supply may be contaminated with typhoid bacilli, and thus propagate the disease. The epidemic at Providence, R. I., in November, 1888, which was traced to the pollution of the water of the river with fecal matter from typhoid cases, 3| miles above the pumping station, is a case in point. The bacilli were found by Prudden and Ernst in the filters of the Providence houses. It is an admitted fact that the disease has often been originated in this Way, but it is a question as to what value this mode of infection has as compared with others. Does the typhoid fever, which is the chief endemic fever of Washington, owe its continued existence to recur- 8 TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. ring or continued infection from this source'? Would we eliminate the disease by purifying the Potomac supply and destroying all its organic life? The Potomac water has been subject to very careful analyses, and, " in general, the water may be said to be in excellent condition and to compare extremely favorably * * * with that of other cities. Its chief defect " is " the presence of suspended clay in the winter " and after heavy rains in any season.* Table V.-Chemical analysis of Potomac water-averages 1888. [Results in parts per million.] Total solids. Nitrogen as- Oxygen con- sumed. Chlo- rine. Free ammonia. Albumi- noid ammonia. Nitrites. Ni- trates. Highest (1888) 164 .0600 .2720 .018 2.32 4.30 5.0 Lowest (1888) 69 .0000 .0320 .000 .08 .76 3.0 Average (1888) 111 .0176 .1190 .000 .97 1.98 4.2 Highest (1889, to September) 192 .0560 .4520 .012 1.80 3.32 5.8 Lowest (1889) 76 .0000 .0600 .000 .50 .88 3.5 Average (1889) 110 .0190 .2140 .000 .82 1.82 4.2 Highest (1889, to September) 270 .3920 .6520 Trace. .8 3.80 5.0 Lowest (1890, October) 80 .0000 .0600 .000 .0 .82 4.0 Average 136 .041 .295 .000 .7 1.85 4.3 Highest (1890, to October) 132 .0140 .1200 Trace. 1.0 3.10 4.5 Lowest (1891, July) 76 .0000 .0200 .000 .3 .56 4.0 Average 104 .0043 .0627 .000 .6 1.97 4.3 Highest (1891-92) 168 .0080 .1600 Trace. .8 3.96 6.0 Lowest (fiscal year) 82 .0000 .0200 .090 Trace. .78 4.0 Average 113 Trace. .0640 .000 .6 1.85 4.3 Highest (1892-93) 159 .0520 .1240 .000 .6 4. 50 5.0 Lowest (fiscal year) 90 .0000 Trace. .000 .5 .78 4.0 Average 125 .0200 .0661 .000 .6 1.64 4.7 The value of the so-called biological analyses of drinking water is, as Theobald Smith says (Medical News, Philadelphia, April 9, 1887), still very unsettled. As the result of one year's observation made by him, a relation was found between turbidity and the presence of bacteria. Bacteria were most abundant in winter, January and February having the highest average; August, September, and October, the months of the greatest prevalence of typhoid fever, having the lowest. Bacteria, most of which were harmless, were most abundant after heavy rains, and their presence in association with turbidity proved the then source to be from the washing of the surface of the soil. In the latest bacteriological report on Potomac water Theobald Smith adheres to this statement, and says that fecal bacteria and turbidity were coincident; that is, that rainfall carries into the Potomac what ever may happen to be on the surface of the soil, clay, manure from the fields, inorganic or organic matter of any sort. The nature of the country through which the Potomac flows, much of it being mountain- ous, as well as the absence of large cities on its banks, diminish the risks of infection from this source. As the country comes more and more under cultivation turbidity and impurity from the washing of * Report of Engineer Department, District of Columbia, year ending June 30, 1892, p. 77. TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. 9 plowed and manure-covered landwill be more common. The possibility of the introduction into the water of the microorganism of typhoid fever is dependent upon its presence in localities washed by the Poto- mac and its tributaries. CONTAMINATED WELL WATER. The question, after all, is not whether typhoid fever can be propa- gated by the drinking of Potomac water, but whether, as a matter of fact, it is usually propagated in this way. Before this question can be determined other probable sources of origin must be considered. It is an unjustifiable conclusion that because fecal bacteria are found in Potomac water, therefore typhoid fever is usually propagated by the drinking of Potomac water. Bacteriology may lead us astray here, and data of a very different sort must receive due weight before a logical conclusion can be reached. Consideration must now be given to the relations of the mortality of typhoid fever and its distribution In different sections of the city to the pollution of the soil by the leakage from privies, and to the drinking of contaminated well water. The truth of the theory may be considered as established that there is a relationship between pollution of the soil with human excrement and the drinking of well water contaminated with the poison of typhoid fever contained in this excrement. The converse of this has also been absolutely proved that typhoid fever can be diminished-almost elimi- nated-by a proper purification of the soil and the drinking of pure water. Facts will be alluded to further on which will illustrate this point. Out of a total of 1,174 squares in Washington and Georgetown deaths from typhoid fever occurred in 426 squares, or one death in about two and two-third squares. If the city is arbitrarily divided into four sections, Georgetown mak- ing the fifth, and the number of deaths from typhoid fever during the last five years be marked in the localities in which they occurred, it will be seen (see Map I) that there is a great difference in the distribu- tion of mortality. In region 1 (all that part of the city south of East Capitol street and the public grounds, including the southeast and southwest parts of the city) there is a very large number of cases. In this area there were 197 fatal cases in 131 squares. In region 2 (east of North Capitol street and north of East Capitol street) in 59 squares there were 84 deaths. In region 3, comprehending all that part west of North Capitol street and east of Thirteenth street and north of the public grounds, in 116 squares there were 179 cases. In region 4, west of Thir- teenth street to Georgetown and north of the river to Florida avenue, in 82 squares there were 114 deaths. In Georgetown in 38 squares there were 52 fatal cases. Assuming that each death represents 10 cases of typhoid fever, in the five years there were about 6,260 cases in 10 TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. Washington, at the rate of over 1,200 cases a year. Of these there were nearly 400 cases a year in the southeast and southwest districts, 170 in the northeast, 360 in the middle region, 230 in the northwest, and 100 in Georgetown, 400 in hospitals and public institutions, and 190 in the county. If we add the cases occurring in hospitals and the county to those in the city proper we have a total of 9,220 cases in five years, an annual average of 1,444 cases. The percentage of deaths from typhoid fever in each of these divi- sions to the contained population is: Region. Population of region. (Police cen- sus, 1892.) Total deaths from typhoid fever in five years in each region. Annual rate of mor- tality to 10,000 popu- lation in each region. I. (South) 62,218 197 6.3 II. (Northeast) 26,278 84 6.2 III. (Central) 70,865 179 5 IV. (Northwest) 49, 969 114 4.6 V. (Georgetown) 16,344 52 6.3 30,429 95 6.2 The interesting fact is to be noted in this table that the annual rate of mortality of the whole District being 6.2, that of the northwest sec- tion is 4.6; central region, 5; south, east, Georgetown, and the county having each the same average, practically, as that of the total District average. The close relation of a soil polluted by sewage to typhoid fever prev- alence is admitted to be a causal relationship, and no argument need here be adduced to support a theory so universally adopted. In Wash- ington and the District there are three modes of infection of the soil with human excreta and sewage: (1) The overflow and leakage from privies. (2) The leakage from defective drain pipes in the soil. (3) The backing up of sewage in the sewers draining the lower parts of the city and the flooding of basements and cellars. The existence of the privy method of disposing of human excreta in cities is sufficient evidence of a contaminated soil. Map No. 4 shows the numerical distribution of the privies of Wash- ington. There are in the city limits 8,959 box privies, 5,133 in the county, a total of 14,092. In the first division (south) there are3,994 In the second division (northeast) there are 941 In the third division (central) there are 1,086 In the fourth division (north and west) there are 1, 761 In the fifth division (Georgetown) there are 1,177 Total 8,959 Squares 743 to 795 in the southeast region may be cited as an exam- TYPHOID FEVER IN THE DISTRICT OP COLUMBIA. 11 pie of the relative distribution of privies and closets with sewer con- nections: Square. Privies. Closets. 743 82 13 766 23 6 768 14 3 770 41 14 799 21 19 795 24 22 289 355 In fourteen squares in the northwest part of the city there were 153 privies and 297 closets. The report of the inspector shows that for the nine years ending June 30, 1891, there were 42,197 full or overflow privies reported, 6,455 boxes with leakage, and 663 old and dilapidated boxes. In one year, 1892, there were 465 boxes noted with leakage. It is difficult to ascer- tain the extent to which the saturation of the soil takes place in this way, but the above facts demonstrate that the saturation with excre- mentitious matter is a necessary result of such conditions. Every report of the engineer department of the District govern- ment contains a statement as to the relaying of pipe sewers. In the year 1892 there were 1,534 linear feet of sewer pipe which were taken up and relaid; 8,438 linear feet of obstructed sewers were replaced. These sewers were faulty in gradient, alignment, and because of defective joints, allowing the intrusion of tree roots, and in quite a number of cases they were of insufficient size. They were all laid under contracts made with the board of public works, in 1871-'74. (Report upon the sewerage of the District of Columbia, by board of sanitary engineers, June, 1890.) All pipe sewers laid prior to 1874 require to be replaced by those of suitable construction, with joints protected by concrete. It need not be added that such defective sewerage conditions permit the satura- tion of the soil with fecal matter. A third cause, which prevents thorough drainage of the soil and adds to the dangers from saturation with sewage, is found in the fact that from the foot of Capitol Hill westerly to the Potomac River there is a long, flat area only a few feet above high tide. To the north and east the ground rises; the soil of the lower area is moist, that of the elevated territory is composed of compact gravel, clay, and loam, and is comparatively dry. Owing to the absence of slope, and, therefore, of scouring velocities in the sewers in the south and east, accumulations take place in the sewers, which are added to by the entrance of tide water. In the Tiber Creek sewer these deposits reached 2 to 3 feet in depth and several thousand feet in length, reaching nearly to the pres- ent District building. The daily effect of the entrance of the tidal current into the sewer is to prevent the complete emptying of the drains, 12 TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. and in times of flood great quantities of noxious sewage is carried into cellars and basements. The drinking of the infected waters of wells has long been known to be a mode of propagation of typhoid fever. If the soil of the city is receiving a considerable portion of the excreta of typhoid cases-if much of that soil is badly drained and wet with returned sewage-is it possible to avoid the danger of the fouling of well water? In that low section of the city in which there is the most imperfect drainage, in which the soil is most contaminated by the defective sew- erage, there are many thousand inhabitants, with 3,994 privies, drink- ing the water from 140 wells. In the southern region, with 197 fatal cases, there were 140 pumps, now reduced to 87; in the northeast, 84 fatal cases and 47 pumps, now reduced to 29; in the middle area, 179 deaths, 70 pumps, now 42; in the northwest, 114 deaths, 34 pumps, now 22. (The number of pumps here given is taken from map published by District Commissioners in 1889, and list furnished May, 1894.) In Georgetown there were 52 deaths, with 18 pumps.* It can be assumed that where there are the largest number of pumps there is the largest consumption of well water; that well water is used most largely by the poor, and in those quarters of the city where the water and sewer connections are fewest; and that Potomac water is used chiefly where the water and sewer connections are most numerous. We know that water from the 310 pumps existing at the report of 1889 was largely used by the people living on the 426 squares in which the 626 fatal cases occurred. Even by those having access to Potomac water, well water is largely consumed, on account of its being colder during the hot months of the year. The object of these considerations is to show that the soil underlying the city is being constantly impregnated with human excrementitious matter, and with all microorganisms therein contained, and that the water of wells liable to be contaminated with such material is being constantly and generally used as drinking water by the people. It is not an assumption that the well water thus consumed is infected and dangerous to health. It is a matter of chemical and bacteriolog- ical demonstration. At the end of 1890 there were 271 public pumps in service; 17 of these were abandoned during the year as being no longer fit for use. In the report of the engineer of the District for 1889-'9O, it is stated * The number of pumps here given, and as shown in map No. 2, is taken from a map published by the District Commissioners in 1889, and from a list furnished by them in May, 1894. The number may not he strictly correct, as errors have been found in the map of 1889. TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. 13 that 75 per cent of the water of wells examined was found to be suspi- cious. In the northwest 71 per cent was bad or suspicious, in the southwest all examined were bad or suspicious, in the northeast 2 out of 3, in the southeast 40 per cent, and in the county 70 per cent. The report adds that the only excuse "for keeping the wells open is the filthy condition of the aqueduct water and the high temperature which it reaches in the mains in summer, often 85 degrees, which is far from palatable to the poorer classes, who are unable to purchase ice." The following year 9 wells were filled and abandoned. In the year ending June, 1892, of 57 wells examined 24.6 per cent were condemned or declared very suspicious; 14 were filled and abandoned. The wells of the county were, as a rule, more contaminated than the city wells, a condition due to the fact that the soil of the city is better drained by sewerage than that of outlying districts. The report for the year ending June 30, 1893, states that a larger number of wells were condemned than in the previous year, " owing to the large number examined from the low portion of the city in the southeast and southwest sections." Fourteen were found dangerous. This is the very section of the city in which the number of fatal cases was so great in the five years. The following report of bacteriological examinations of 13 wells, made for the committee by Dr. J. J. Kinyoun, fortifies these views of the gen- eral unhealthfulness of the well waters: Sample No. Location of well. Result of examination. Condition of water. Recommenda- tions. 1 East side Seventh street be- Sewage bacteria. Colon Bad tween M and N streets NW. bacillus isolated. closed. 2 do ... ............... do Do. Seventh NW. 3 do . do ....... Do. tween M and N. 4 Tenth and S streets N W Sewage bacteria. Fecal bac- do Do. teria. Colon bacillus iso- lated. te, 5 Sixteenth and Corcoran streets Ordinary forms usually Good NW. found in water. under observa- tion. 6 Seventeenth and K streets Ordinary forms usually Suspicious.. Do. F NW. found in water, but in considerable quantities. 7 Tenth street between B and Sewage bacteria. Colon Bad Should be closed. CNE. bacillus isolated. 3 Third street and Indiana ave- Sewage bacteria do Do. nue NW. 9 T and Eighteenth streets NW. Ordinary water bacteria, Suspicious.. Should be kept but in large numbers. under observa- tion. 10 Twenty-third and G streets Sewage bacteria Bad Should be closed. NW. 11 Eighteenth and S streets NW. Sewage bacteria in great ... -do Do. numbers. 12 K street between Twenty- Sewage bacteria. Colon do Do. first and Twenty - second bacillus isolated. streets NW. I 13 Ninth and H streets NW Ordinary water bacteria in Good small numbers. under observa- tion. In the recently published report of the examination of the water of the city wells by Drs. Theobald Smith and Mew, 16 wells were reported 14 TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. as examined bacteriologically by Dr. Smith, and the conclusions reached were favorable to the general purity of the well water. Five wells only were found to contain fecal bacteria; the water of 4 was in good condi- tion, and that of 7 in need of improvement. The suggestion is made by Dr. Smith that the wells upon which a favorable report is made should be retained, that others should be improved, and that bacteriological examinations should be made at least once a year to determine the fitness or unfitness of the water for drinking purposes. He also suggests that wells considered safe should be so labeled. But is not the fact that some wells at a particular date contain fecal bacteria a sufficient reason for condemning the whole system? As long as causes of soil pollution exist, is not one well as liable, or nearly as liable, to contamination as another? And the fact that one well contains no bacteria, another a few, and another many, is no proof that.all are not liable in different degrees to become at some time infected. To be under the necessity of labeling each particular well as healthy or unhealthy, after annual examination, is an endless task and a most unscientific procedure, for how many individuals who wish to quench their thirst will be influenced by the published statement impugning the reputation of a particular well? Even if the individual knows that bacteria are found, he will drink and take the risk. As sanitarians we must condemn the whole system, and advise an early abandonment of all wells as the only solution of the question. The advice contained in the report made to the Sanitary League we believe to be mischievous, and to involve a continued menace to health. It should be remembered that the water of the 16 wells reported upon by Dr. Smith is of those which have been permitted to stay, and that over 80 have within the last five years been condemned and filled up. Dr. Kinyoun finds sewage and fecal bacteria in 9 out of 13 examined. For how long a time will these now reported upon as free from fecal bacteria remain so, with the continued presence of typhoid fever among us? Shall we wait for the infection to take place, or shall we remove the possibility of the dissemination of the disease in this way? These are questions to which we should give no uncertain answer. The lesson of Vienna should teach us what this answer should be. From 1851 to 1874 well water of an impure character was used to a large extent. During this time the deaths from typhoid fever ranged from 10 to 34 annually in every 10,000 of the population. In 1874 spring water of great purity was introduced, and the well water of impure wells was given up. The annual mortality rate immediately fell to 5, and in three subsequent years to 1.1. A good sewerage system was in existence long before this, but it had no effect in reducing the mortality, as sewerage without the abandonment of the drinking of infected well water is without effect. TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. 15 One fact to which separate attention should be drawn is that many of our cases of typhoid fever are imported from without. At the end of the summer it is a frequent occurrence for the disease to develop in individuals who have just returned from seashore and other resorts, and a much larger number of our inhabitants go out of town now than for- merly. This is one means by which our mortality is increased, and fresh infection is added to that already existing. INFECTION THROUGH MILK. The dissemination of typhoid fever by the milk supply in the District has not been investigated fully enough to warrant any extended remarks or conclusions. It would be well to make this a separate matter of study. It is safe to assume, from the experience of many observers elsewhere, that typhoid fever is to a certain extent propagated by milk; there is nothing in the condition of the dairies from which our supply is drawn to make us think that we are better protected from this dan- ger than other communities where epidemics have been traced to milk infection. There are 65 distinct places in the District where cows are kept and from which milk is supplied. CONCLUSIONS. It has been shown that in Washington there is a coincidence be- tween a soil polluted with the leakage of the excreta from typhoid fever patients, the drinking of infected well water, and an extensive distribution of typhoid fever; that where these two first conditions exist to the greatest degree typhoid fever is most prevalent. It remains to be seen whether the purification of the soil, and the abolition of the water supply from pumps, would lessen the disease. The belief that typhoid fever spreads by " soil contamination" would be much strengthened if other cities, with the same conditions, have diminished the percentage of the disease by draining the soil and abandoning the use of well water. (1) Typhoid fever increases in proportion to the saturation of the soil with decomposing organic matter, especially human excreta, and to the drinking of infected well water. (2) Typhoid fever decreases in proportion as a city is well sewered, and in proportion to the abandonment of the drinking of well water and of all contaminated water. The greatest diminution in typhoid fever has taken place in England and Germany, where expert engineers and liberal municipal govern- ments have combined in the work of sewering the principal cities. In the cities of Spain, Italy, Russia, and Mexico, where the sewerage sys- tems are less complete, the diminution has not taken place. The history of Munich offers the strongest evidence on this point. 16 TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. From 1854 to 1859, when no means existed to prevent the fouling of the soil, the mortality was 24 to 10,000 inhabitants. From 1860 to 1865 the sides and bottoms of the pits of the privies were cemented, and the mortality fell to 16.80. From 1866 to 1873, with partial sewerage, it was 13.30; from 1874 to 1880, with improved sewerage, it was 9.26, and from 1881 to 1884, with still greater improvements, it fell to 1.75 to 10,000 inhabitants. The experience of Berlin is very instructive to Washington, as showing the difference in mortality in houses with sewer connections and in houses without them where privies were used. In houses with sewer connections there were 15.5 cases and 4.5 deaths to 10,000 population. In houses without sewer connections there were 56 cases and 17.9 deaths. In sewered houses there was 1 case to every 49.3 houses and 1 death to 137.5 houses. In nonsewered houses there was 1 case to every 9.3 houses and 1 death to 43 houses. In Dantzic, with a wretched system of privies, there were 10 deaths to 10,000 inhabitants. The introduction of an abundant water supply in 1869 produced no effect on the death rate. The city was sewered in 1872. In the following twelve years the average mortality was 2.4 and in the last five years was only 1.5. In Breslau in 1866, without sewers, the mortality was 15.2; in 1876, with sewers, it dropped to 5.5 to 10,000 inhabitants. In the cities of England, before any extensive sewerage systems were introduced, from 1850 to 1871, the mortality was 9; from 1876 to 1884, it was 3.6, the change following upon a general introduc- of sewer drainage. Chart ii, which accompanies this report, illustrates in a most strik- ing way the differences in mortality in sewered and unsewered cities, the percentage being to 10,000 population in five years, 1880 to 1884. In cities with good sewers and general water supply the averages were as follows: Munich, 1.7; Dantzic, 1.5; Frankfort, 1.4; Breslau, 3.3; Hamburg, 2.6; Berlin, 2.9; Brussels, 3.3; London, 2.3; 28 English cities, 3.2; New York, 3; Brooklyn, 1.5; Vienna, 2.1; Washington, 4.6; Washington (1885-1890), 6.7. In cities without sewers or very imperfectly sewered the yearly aver- ages for each 10,000 residents were as follows: Paris, 9.9; Marseilles, 12.8; Turin, 9.5; Naples (1881-1884), 7.1; Palermo (1881-1884), 13.1; Catania, 19; 281 cities in Italy (1881-1882), 9.5; St. Petersburg (1883- 1884), 9.9; Biga (1881-1882), 15.8; Budapest (1877-1881), 9.2; 20 Ger- man cities (1878-1882), 9.8; New Orleans (water supply from cisterns above ground), 2.7; Baltimore (abundant water supply), 4.8; Cincin- nati, 7.3. Chart in shows the reduction of mortality as a result of sewerage. Brooklyn and New York have the best sewerage systems in this country. New York has 300 miles of sewers, but Brooklyn is perhaps the best sewered large city. New York has a mortality of 3 and Brook- lyn 1.5. The mortality of Brooklyn, our best sewered city, is lower Chart III. -Deaths from typhoid fever to each 10,000 inhabitants before, during, and since the introduction of sewerage and water-supply. TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. 17 than Munich, Berlin, Hamburg, London, Vienna, which are the best sewered cities of Europe. And when a city is said to be sewered this means that water-closets are substituted for privies and the soil is kept free from contamination. To turn, now, to other cities in this country, Baltimore, as Osler in his excellent report says, "has practically only surface sewerage. * * * The excreta pass, for the most part, into privy pits, of which it has been estimated there are from 70,000 to 80,000, occupying one- twentieth of the entire surface of the city, exclusive of streets and parks." Leakage, he says, unquestionably occurs in a very large num- ber, with saturation of the ground in the vicinity. Baltimore has a mortality of 4.8, more than three times that of Brooklyn. Washington, whose sewerage system is very good in most respects, but with fatal defects which diminish its efficiency and with that equally great danger from soil pollution from its 9,000 privies, has an average annual mortality of 6.2 in the last thirteen years. This is four times the death rate of Brooklyn, twice that of New York, and the same as that of Philadelphia. The daily pollution of the soil by the fecal discharges of our patients suffering from typhoid fever, with the resulting contamination of well water, must be recognized as. the chief source of the diffusion of the disease. It is a case of auto-infection. We are daily breeding the poi- son which poisons us, and the inevitable round from intestine to soil, from soil to well, and from well back to intestine goes on and on with the most tragic uniformity. We sustain all the conditions favora- ble to rapid and perfect propagation of the bacilli. Granches and Des- champs have experimentally shown that typhoid germs placed on the surface of frequently moistened ground will penetrate nearly 2 feet into the soil, and will there retain life for five and a half months. They multiply rapidly in illy drained soil, live for an indefinite time in privy vaults, and have a much longer existence in cisterns and wells than in running water. In Washington we supply all these necessary conditions-leaking privies for the reception of the excreta and their contained germs, a damp and illy drained soil for their reception and rapid growth, neigh- boring wells for the resulting, the inevitably resulting, contamination of drinking water consumed by a thirsty population. What more con- veniences can we supply1? What more successful means can we adopt to raise our mortality to a noinhJxLaibtwi +,h mt of Brooklyn, New York, iUwHBoswn? We are among the most successful cul- tivators of the deadly bacillary plant in this country. Recommendations. H The committee would urge apfrhxtjie Medical Society the importance of taking thelrntiative in the efforvX? tmutbsLthe spread of this H. Mis. 188-- 18 TYPHOID FEVER IN THE DISTRICT OF COLUMBIA. destructive but preventable disease by urging upon our municipal gov- ernment and upon Congress the prompt adoption of measures to /iTuiio vc the eattags Lu has drawnattention. ~ be recommended~jM»e4 1. The immediate abandonment of all wells within the city limits, exception only to be made in case of the absence of the Potomac supply, and where the wells, after repeated chemical and bacteriological exam- inations, have been found to be free from all possible sources of dan- ger. But even these to be abandoned as rapidly as possible. 2. Purification of the sewerage system already existing, by replacing as rapidly as possible all damaged or defective drains. 3. The introduction of new sewers in advance of other improvements tin parts of the city not now supplied with drainage, and the extension |of the system as far outside of the city limits as the rapidly growing [population demands, so as to prevent soil contamination. 4. The adoption of some system by which the lower sections of the |city can be more completely drained and the risks arising from the | backing up of tide water and sewage prevented. I 5. The final and safe disposal of the sewage. 6. To make all existing privies, vaults, or other receptacles of human excreta water tight, and by rigid inspection and penalties to prevent the danger from leakage and overflow. 7. The early completion of the plans recommended by Col. Elliot, in charge of the Washington aqueduct, and now in course of execution, which have in view the sedimentation of the Potomac water, and ulti- mately the completion of works for filtration, the only proper method of purification. 8. The suppression of all privies and the enforcing of the law to make i sewer connections. i 9. Careful inspection of all dairies in the District from which our \milk supply is drawn, and the enactment of a law by which no milk Shall be sold in the District without a permit from the health office. The inspection should cover an examination at the dairies of all possible ,sources of infection, water supply. / lOTThe urging of the profession of a careful colla- tion of all facts bearing upon the mode of infection in each case, and the advantage of reporting such facts to the society, and the propaga- tion of the doctrine that immediate disinfection of the stools is the first duty of the physician as guardian of the health of the community. G. L. Magruder, W. W. Johnston, i C. M. Hammett, \ Committee. WIDTH «F 5THEETS AXD South zzzzzz-~-~-''\, , : s« »• ri »< iSSSL?-ii A - .;• • - '.'< Avervxies , - s - ~5zl - =% x"x No. 1. COTY OF WASHINGTON Deaths in Residences within the City! limits from Typhoid Fever na and Malarial Disensesea IH8H to I«»2. inelusive : DEATHS BY DISTRICT*. Malarial I'lF1>ht>id. l>Urewa. Diatnct No. 1 I07 143 • 2 M 46 - ''3 170 86 « - 4 114 78 -6 21 Total. 826 383 - WIDTH AVKNtlE.S' North ABCOCrOM I n U MN 0 *.O * 5t U.V A South East TM'-V-?. «IZS*S«7»* >0'1 a ts 4 '54l7«9 1O2IU2S2A- U 2 3 H! S t 7 4 9 » H HO OU» it t CT 0/9UZlSUUU24 27 Ammu •« ' a, /*>•■* «r •• m-'-- - AOw r... Z M ». «r] »>««.>. - -»»A I SM.fv.« * j* «. 9» No. 2. r IT OF mraiNUTO PUBLIC PUMPS WITHIN TH£ CITY LIMITS. Taken from Map published by the Bistrlet Com- missioners, 1889, and from a list furnished May, 1894. PUBLIC PUMPS IN WASHINGTON ANO GEORGETOWN. ttifi* ISU4 District No. 1 127 80 38 " 2 41 30 11 " 3 70 43 27 " 4 33 21 12 " * fi 18 18 0 Total. 280 201 88 WIDTH North "* 0 £ ® ■ 2..XX ° W*3t ±At?A_ I / i unit 7 • • m n a 3 sim tin »/itovnixwax n «. -..u-. •• ~-«»*»> jtjk Avnu»»tw 2-'--~ ~~ « ' • £ H. z^"^=z zr.:~~ z|SE„ No. 3. i CITT OF WASHINGTON HEATHS FHO.V DIAHHIHEAL DHiASES IN RESIDENCES WITHIN THE Cl Y LIMITS EHOM 1KSS TO ISD2. INCH' ll'E. -WIDTH <»'-STHEETSANl, AVENGES. North '/Ct'AVA * B C O t f C H K L MHO.P O * S tu.v East t I I }4 4 w ?< West < / 2 j * i • • • » « » n J a"* a tta »r9totini3UUMTr t<m. -■« fc. =-- ;ter 1A 'A No. 4. OTT OF WASH! W1W BY S(fCARES, SHOWING THE NVMBER OF BOX PRIVIES. 18f)i. Mrlft by IHntrirti. ffvjr No. 1 3.994 In Washington. 7.782 " 2 941 " Georgetown. 1.177 ■' 3 1.080 " County 6.133 " 4 1.761 " 6 1.177 TOt<i 14 092 Total. 8.969 WIDTH <r STHEET.S ASU . North AOCDCfOHi KLM.NO* Q * 5 T u V £ , South i t C O C r ~ ' u *c p &* ''A I 'j-.-.aA; * l I «.« » • J0J121B £•«! West i I 1 j 4 At » 4 7 » • » It a a stjA n tart Av«rvu»» 'i'll = ■ i=i « 1 *» ■ I elf Z rJZ... M.wa • VteaMOT I •» No. 5. CITY OF WASHINGTON OLD WATER COURS ES.