r FALL U. S. DEPARTMENT OF HEALTH, EDUCATION, AND WELFARE Public Health Service Environmental Health Service ------- Office of Air Programs Publication No. APTD-0884 ------- iJcnce-^v.-tuckct, "£"/ "odford, Fall P.iv&r Air Pollutant Fm'ssion Inventory Prepared by: David V. Mason u.s. nuFAnriEiiT or i PUKUf HiZALTH SERVICE cioiimer Protection ar F:\LTi!, EirjCATION, A'10 VFLFAP.E d Unvircn^entol flcalth 'Service tion 'J Air Quality an> biiission -"!'Vl;a division jLirhs"'., liorth r-rolirra February, 15G9 ------- ACKNOWLEDGMENTS He acknowledge v/ith appreciation the contributions of the many agencies in the gathering of the data in this report. In particular, we are grateful for the use of data and personnel assistance furnished by the following: 1. Massachusetts State Health Department 2. Rhode Island State Health Department. ------- TABLE or COI;TF.I-:TS Paqe PREFACE - 1 INTRODUCTION ' 3 SUMMARY OF EMISSIONS .-.-5 STUDY AREA ,8 GRID" COORDINATE SYSTEM 13-: DISCUSSION OF RESULTS 15 Fuel Combustion by Stationary Sources 15 Transportation Sources 16 Refuse Disposal Sources...., , 17 Industrial Process Sources ~.. 18. Point Source Emissions vs. Total Emissions... 18 METHODOLOGY ' 35 Fuel Consumption by Stationary Sources 35 Transportation Sources 36. Refuse £1 spcsal Sources 36 'Industrial Process Sources 36 EMISSION DENSITY !?Y GRID 45 ------- TABLES Table 1 Table 2 Table 3 Table 4 Table 5 Table G Table 7 Table 3 Table 9 Table 10 Table 11 ASB .Table 12 Table 13 . Table 14 . Table 15 Table 16 Total Er.nssions by Category , Population Characteristies of Providence Study Area Number of Industrial Establishments . in Providence Study Area....'....,..,.., Fuel ni.l Consumption in Study Area..., Coal Consumption in Study Area f-iatural Gas Consumption in Study Area Chemical Analysis of Fuels Pace . 7' . 9 . 12 . 19: . 20 . 21 . 22 . 23 24 27 Sur.suary of Emission from Stationary Sources Vehicle-Miles Traveled in Providence Study Area ,.., Gasoline and Diesel Fuel Consumotion., Air Traffic Activity at Tv;o Major Ai rpo rts , 28 Summary of Transportation Emissions... 29 Refuse Disposal Balance in Study Area. 30 Sol id Waste 'Emi ssions '. ' 34 Summary of Emissions by Point Source.. 38 Summary of'Total Emissions by Grid 41 ------- n1"' T> i.iij!\ Figure 1 Figure 2 Figure 3 Figure 4 Figure 5 Figure 6 Figure 7 Figure 3 Pago Providence, Mew Bedford, and Fall River Study Area 4 Providence Study Coordinate System 14' Point Source Location 37 Sulfur Oxide emission Density Map 46 Participate Emission Density Man 47 Carbon Monoxide emission Density Hap -43 Hydrocarbon Emission Density nap 49 Sulfur Oxide Emission Density r?.p......... 50 ------- PREFACE Tin's report which presents the emission inventory of the Providence, Fall River and New Bedford area is another in a series of studies outlining the sources and emissions of air pollutants for major metropolitan areas of the country. These reports provide estimates of total emissions of oxides of sulfur, oxides of nitro- gen, hydrocarbons, carbon monoxide and particulate matter. The emissions of these pollutants are delineated with respect to source type, season of the year as well as their geographical distribution within the area. These surveys are intended to determine the present . level of emissions and the status of thsir control. The general procedure of these surveys are based on the rapid survey .technique. The study area is divided into grid zones that serve as a basis for locating sources and reporting their emissions. All sources of pollution are classified into two general groups, i.e., point sources and area sources. All sources that emit large quantities of air pollutants are considered individually and located specially within the area. This group which generally contains about fifty to one hundred sources typically includes large industries, power plants, and refuse burning facilities. The remaining sources are considered collectively as area sources and their emissions are reported as totals for grid zones. This group includes motor vehicles, home heating, small industries, on-site refuse, etc. The emissions in both cases are expressed in terms of tons per average annual, summer and winter day. Emissions for the most part, are estimated using various emission . .. factors that are related to these. This means that information and data are collected on fuel consumption and refuse burning rates, vehicle- miles and gasoline consumption as well as various production data. These ------- are then'translated into emission estimates by use of average emis- sion factors. These factors, for the most part, represent average emission rates for a particular industry or fuel type. Because of the inherent differences in type of equipment, operating rates,-con- trol equipment, and efficiencyof operation among the plants and *. ' fuel users within a given category, the application of the emission factors to any individual plant or even a smaller number of similiar plants or processes may result in a discrepancy between the actual and estimated emissions. However, the estimates of total pollutants from all sources in the study area should be fairly accurate. - 2 - ------- INTRODUCTION The information and data presented in this report v/ere gathered,in cooperation with the Massachusetts Health Department and the Rhode Island Health Department during the survey conducted «* - -^ in late October, 1968. The data obtained in this study is for the most part representative of 1967 and emission estimates presented herein should be considered as showing the levels and conditions during 1967. - For purposes of this survey a Study Area consisting of a por- tion of Massachusetts and Rhode Island was selected. The Study Area includes three Standard Metropolitan Statistical Areas (Provi- dence-Pav/tucket, Fall River, and New Bedford).. A 1967 population of about 1.2 million people and some 1,000 square miles, are included in the Study Area.. The Study Area was subdivided into 62 grids made up of two sizes: 25 square kilometer grids in the heavily populated and indus- trialized areas and 100 square kilometer grids in the more rural sections. Using this grid system,information-was gathered on three types of area sources and over one hundred large industries and fuel f users of which about 45 are being considered point sources in this survey. ; ... - -^J .- -- - 3 - ------- MASSACHUSETTS a o -7 1 FRANKLIN " BELLI NGHAM / BLACKSTONE[ ____. MILLVILLE | / \ WOONSOCKET COVENTRY . iSMITHFIELO = 1 ELD . FALLSNlfY / .r-\ PAWTUCK ATTLESOROUGH x- ATTLE8ORO LINCOLN 1 .,' ATI \CENTRAL7 . PAWTUCK6T NORTH1 \-~ \ ,PROVIDENCE I JOHNSTON L- N EAST /G'REENWICH i: .((JAMESTOWN " ' \MIODLE- 10 15 mi les Figure 1. Providence-Pawtucket, Fall River and New Bedford Study Area. -4 - . ------- SUMMARY OF EMISSIONS Over an estimated 700,000 tons of the five major pollutants are emitted annually in the Study Area. Breakdowns of this total with respect to specific pollutants as well as the type .cf sources emitting the pollutants are given in Table 1 and briefly summarized 6elov/. Pollutant Type Oxides of Sulfur: Total tons per year Electric Generation Residential Fuel Use Industrial Fuel Use Commercial Fuel Use Other i 117,800 56% 21% ' 16% 4% 3% Particulates: Carbon Monoxide: Total Tons Per Year Electric Generation Open Burning Road Vehicles Industrial Fuel Use Incineration Industrial Process Other Total Tons.Per Year Road Vehicles Open.Burning Other 22,600 47% 15% 11% 9% 8% 5% 5% 435,400 93% 4% 3% ------- Hydrocarbons: Total Tons Per Year Road Vehicles Evaporation Balance of Transportation Open Burning Other 54,300 56% 37% 3% 2% Oxides of Nitrogen: Total Tons Per Year Electric Generation Road Vehicles Industrial Fuel Use Open Burning Other 64,200 49% - 33% 9% 4% 5% Emissions by Point Sources Oxides of Sulfur Particulates Carbon Monoxides Hydrocarbons Oxides of Sulfur 81,500 T/Year 13,500 T/Year 8,200 T/Year 2,200 T/Year 32,700 T/Year - 6 - ------- TABL'E I/SUMMARY OF AIR POLLUTANT EMISSIONS IN THE PROVIDENCE STUDY AREA, 1967 (TONS/YEAR) Source Category Transportation Road Vehicle Evaporation Other . . . Combustion of Fuels From Stationary Source Industrial Steam-Electric A Residential Other Refuse Disposal Incineration Open Burning 'Industrial Process Emissions 'Grand Total Sulfur . Oxides 2,450 1 ,650 . 800 115,100 19,200 66,100 ' 24,900 4,900 200 200 Neg. 50 117,800 Parti c- ulates 2,800 2,600 200 13,500 2,100 10,600 600 200 5,200 1 ,800 3,400 1,100 22,600 Carbon Monoxides 415,500 407,900 7,600 700 100 , 400 I 200 fleg. ; ! 19,200 1 ,000 18,200 Neg. 435,400 . Hydro- carbons 51,900 30,400 19,900 1,600 1,200 100 500 .600 Neg. ' 1,200 100 1,100 Neg. 54,300 Nitrogen Oxides 22,100 21,500 600 39,500 5,500 31,500 1,200 1 ,300 2,600 250 2,350 Neg. . 64,200 ? 5 ------- -S. *.-.**-LA. . STUDY AREA As shown in Figure 1, the Study Area lies around Narraganset.t Bay and along Rhode Island Sound. There are 48 cities and towns in the Study Area. Twenty-eight are in Rhode Island while the remainder are situated in Massachusetts. The total area of this region is about 1,000 square miles of which approximately 270 square miles can be considered urban. Included in this urban portion are the cities of East Providence, Pawtucket, Warwick, Fall River, North Providence, Providence and New Bedford which collectively have some 600,000 inhab-. itants. The 1960 and 1967 population of each of the forty-eight cities and towns are shown in Table 2. Campari son of the tv/o populations shows an average increase of 7.0 percent for the Study Area as compared to an increase of.10,9 percent for the United States during the same period. The major manufacturing industries of the Area.are those_ concerned with textile products and metal products. The number of establishments by industrial category are suiranarized for 1960 in Table 3. The proximity of the Narragansett Bay and the Atlantic Ocean plays .j... an important part in determining the climatef°r Providence' and vicinity. In winter, the temperatures are modified considerably, and many of the storms drop their precipitation in the form of rain rather than snow. In summer, the days are often cooled fey seabroezes - 8 - ------- TABLE 2 POPULATION FIGURES FOR PROVIDENCE-PAWTUCKET - FALL RIVER, AND NEW BEDFORD StISA'S Providence . Pawtucket SMSA Rhode Island "Portion Barrington Bristol Burrilliville Central Falls Coventry Cranston Cumberland East Greenwich East Providence Jamestown Johnston ; Lincoln Marragansett North Kingstown North Providence North Smithfield Pav/tucket Providence Smithfield Warren Harv/ick West Harv/ick Woonsocket Massachusetts Portion 1960 821,101 731,146 13,326 14,570 9,119 19,858 15,432 66,766 18,792 6,100 41 ,955 2,267 17,160 13,551 3,4,44 18,977 18,220 7,632 81,001 207,498 9,442 8,750 68,504 21,414 47,080 89,743 1967 887,230 777,020 16,530 15,890 9,790 18,900 17,820 72,700 24,100 8,300" 45,300 2,590 19,750 14,750 5,100 23,300 21,400 8,800 78,300 189,000 12,150 9,860 73,500 22,140 47,300 110,210 Percent Increase 3 6 19 9 7 -5 15 8 28 - 36 7 14 15 8 48 23 17 15 -3 -9 29 13 15 3 1 23 - 9 - ------- TABLE 2 POPULATION FIGURES FOR PROVIDENCE-PAUTUCKET FALL RIVER, AND NEW BEDFORD SiMSA'S Attleboro Bellingham Blackstone Franklin Millville North Attleborough Plainville Rehoboth Seekonk Wrentham . . . V:v^ Fall River SMSA Massachusetts Portion Fall River Somerset - Swansea '.'Jsstport Rhode Island Portion Tivertown New Bedford SMSA . Acushnett Dartmouth Fair'naven 1960 27,118 6,774 5,130 10,530 1,567 14,777 3,810 4,953 8,399 6,685 138,156 128,695 99,942 12,196 9,916 6,641 9,461 9,461 143,176 5,755 14,607 14,339 1967 29,110 12,200 6,410 16,400 1,730 16,000 4,480 5,700 10,500 7,680. 151,780 140,650 103,000 16,350 12,500 8,800 11,130 11,130 148,480 7,130 17,600 16,300 Percent Increase 7 80 25 56 10 8 18 15 25 15 "' 10 9 3 34 26 33 18 18 4 24 20 14 ------- TABLE"2 POPULATION FIGURES FOR PROVIDENCE-PAHTUCKET ', FALL RIVER, AND NEW BEDFORD SMSA'S Nev/ Bedford Marion Mattapoisett Extra Rhode Island Towns James to v/n Middle town . Newport Portsmouth 1960 102,477 2,881 3,117 2,267 12,675 47,049 8,251 1967 99,500 3,630 4,320 2,600 19,790 36,300 10,780 Percent Increase -3 26 39 15 56 - 23 31 Study Area Totals 1,172,675 1,254,620 - n - ------- TABLE; 3 NUMBER OF ESTABLISHMENTS IN THE PROVIDENCE, - .'NEW BEDFORD & FALL RIVER SHSA'S (1960) Food Products Textile & Leather Products Paper & Printing Chemicals & Petroleum Lumber and Wood Products Stone & Clay Products Electrical Machinery Transportation Metal Products . » Miscellaneous Providence 52 236 68 67 14 5 . 80 13 139 262 New Bedford 14 89 5 4 2 1 11 7 10 i 5 Fall River 14 139 12 9 2 2 6 1 8 2 ------- GRID COORDINATE SYSTEM Grid coordinates based on the Universal Transverse Mecator System were used in this study to show the geographical distribution of sources and emissions. As shown in Figure 2, the entire Study Ar-23 was divided into 62 grids of 2 different sizes--25 square kilo- meter, and TOO square kilometer. Different size grids are used to limit the number of grid zones and yet allow a satisfactory definition of geographical gradation of emissions in areas where the majority of pollution occurs. For this, reison, the 25 square kilometer grids zones were placed in downtown - areas, where the density of emissions changes abruptly within short distances. In areas primarily rural in nature, the use of small zones was not as important. As illustrated in Figure 2, each grid line is identified by a coordinate number. The north-south and east-west coordinates, are expressed in meters. The point sources are identified by the X-Y coordinates to the nearest 100 meters. The grids are identified by the X-Y coordinates of the geographical center of the grid. - 13 - . ------- : 4,630,00° -. 4,620,0°° 4,610, 00° 4,600,000 Figure 2. Grid system of Providence Study Area. - 14 - ------- DISCUSSION OF RESULTS All sources of air pollution considered in this survey fall into ; one of the following four categories: i - 1. Fuel consumption by stationary sources ? 2. Transportation sources j 3. Refuse disposal ' 4. Industrial process losses Each of these categories are dealt with individually in this section ;; and in the subsequent section where data .sources are given and techniques -: of calculation are discussed. In addition, the emissions from.the point : sources are compared with total area source emissions, - i It is important to note that the estimates presented herein and especially in the process loss category are, in most cases, partial totals. This stems from the inavailability of emission factors as well as appro- [ priate production data. In the case of hydrocarbon emissions'where gaso- ''.- i , line evaporation was included but solvent evaporation was not, the totals are considerably lower than the actual values the results should, there- ; fore, be viewed with these limitations in mind. £ u i Fuel Combustion by Stationary Sources j:, Tables 4 through 6 present the consumption of fuel oil, coal and (-. t natural gas within the Study Area. As shown .in these tables, fuel oil ! ; is the primary fuel used in the Area with coal and natural gas..ranked | second and third. During 1967, over 500 million gallons of fuel oil, \ 1.7 million tons of coal, and 25 billion cubic feet of natural gas were 1 burned in the Study Area. In terms of the total energy supplied, fuel ; oil accounted for 51 percent, coal 30 percent, and natural gas 19 per- j cent. The average chemical characteristics of the fuel are. summarized I. in Table 17; I - 15 - ------- The power generating plants are the largest users of fuel in the Area.. During 1967, they consumed 48 percent of the fuel oil and 94% of the coal. There are no natural gas operated power plants in the Area. The industry in the Area is moderate in size and only consumes 22 percent of the fuel oil and 10 percent of the natural gas. Natural gas and fuel oil are both used quite heavily for heating of homes and offices. Over 12 x 1012 BTU's from natural gas and 20 x 10^ BTU's from fuel oil are used for this purpose. Coal is used very sparingly. The emissions resulting from the burning of these fuels are sum- marized in Table 8. The use of fuels is the largest source for three out of five of the pollutants: sulfur oxides-97 percent, particulates- 56 percent and nitrogen oxides-58 percent. The burning of fossil fuels is an insignificant source of carbon monoxide and hydrocarbons, emit- ting only 0.2 percent and 2.0 percent respectively.- Transportation Sources In all, three types of transportation sources were considered. These include motor vehicles, aircraft and railroads. Vessels were not considered because of a lack of information. Tables 9 and 10 summarize vehicle miles and gasoline-diesel fuel consumption data which were used to calculate the emissions from motor vehicles. About 13 million vehicle miles of travel occur per day within the Study Area, of which about 2 percent is accounted for by diesel powered vehicles. This rate of travel consumes about 350 million gallons of gasoline and 10 million gallons of diesel fuel annually. There are two major airports within the Study Area. The air _ ,\/ traffic activity at each of theseT. F. Green State Airoort ano HEW . Bedford Airport--is summarized in Tables 11-A and 11-B. - 16 - ------- Approximately 210,000 itinerant operations and 190,000 local oper- ations took place during 1967. A local operation is defined as a take-off or landing that originates and ends at the same airport. An itinerant operation is one that either originates or ends at the airport. Air carrier flights are primarily commercial, while gen- eral aviation includes all private and pleasure flights. The third category in transportation, railroads, is by comparison minor. During 1967, an estimated five million gallons per year of fuel (diesel) were consumed in the Study Area. The emissions from transportation sources are summarized in Table 12. Gasoline powered vehicles are by far the most significant source of air pollution. In 1967, they accounted for 98 percent of carbon monoxides, 93 percent of the hydrocarbons, 91 percent of the oxides of nitrogen, 69 percent of the particulate matter-and 57 percent of the sulfur oxides (of the total transportation emissions.) Diesel powered vehicles were an important source in particulate emissions. The emissions from aircraft, although minor overall, may be sig- nificant in that the emissions occur at two locations rather than throughout the Area as is the case in motor vehicles travel. Refuse ^Disposal Sources The estimated pattern of refuse disposal for the Study Area is summarized in Table 13. About 35 percent of the refuse is disposed of .by open burning and 25 percent by sanitary landfills with the remainder being disposed of in incinerators or dumps. .These are rough estimates and should be considered as such. The emissions from burning of refuse is summarized in Table 14. On-site open burning, is the primary source in the category. - 17 - ------- Industrial Process Source Industrial processes do not contribute substantially to the overall emissions in the Providence, New Bedford, Fall River Study Area. The largest emitters in the Area are grey iron .foundries and concrete batching facilities. Both together contribute about 1,000 tons of particulates per year. There is also a sulfuric acid plant that has an estimated emission rate of 50 tons sulfur oxides per year. Point Source Emissions Vs. Total Emi ssions Point source emissions which include both fuel burning and pro- cess infromation are presented in Table 15 . Point'sources collectively account for the following percentages of the total pollutants: Sulfur Oxides 72% Particulates - 2% Carbon Monoxides 2% Hydrocarbons 4% Nitrogen Oxides 50% - 10 - ------- TABLE 4 FUEL OIL CONSUMPTION BY SMSA 1967 (bbl./Year) Providence New Bedford Fall River Total Residential Commercial Industrial Utilities Total 2,550,000 490,000 2,000,000 1,800,000 6,840,000 440,000 90,000 400,000 3,100,000 4,030,000 370,000 80,000 300,000 .800,000 1,550,000 3,360,000 660,000 2,700,000 5,700,000 12,420,000 ... - 19 - ------- TABLE 5 COAL CONSUMPTION BY SMSA, 1967 (TONS/YEAR) Residential Commercial Industrial Utilities Total * Providence 56,000 Neg..*~ 14,000 160,000 230,000 New Bedford 10,000 Neg. MA** Neg. 10,000' Fall River 10,000 Meg. MA . 1,460,000 1,470,000 Total 76,000 Meg. 14,000 1,620,000 1,740,000 *Neg. - Negigible ; **MA - Mot Available .. i .. i ; :.: !. - 20 - ------- TABLE 6 NATURAL GAS CONSUMPTION BY SMSA 1967 (MILLIONS CUBIC FEET/YEAR) Residential Commercial Industrial Utilities Total Providence 12,500 3,400 1,500 Neg. * 17,400 Nevj Bedford 3,200 500 700 Neg. 4,400 Foil River 3,000 500 600 Meg. 4,100 Total 18,700 4,400 2,800 Neg. 25,900 *Neg. - Negligible - 21 - ------- TABLE 7 CHEMICAL ANALYSIS OF FUELS IN THE PROVIDENCE STUDY AREA, 1967 Fuel Sulfur %: Ash&-.- Volatile %. j. Coal . 0.7 5 j; Residual Fuel Oil 2.25 j- Distillate Fuel Oil 0.24 ! ** Gas 0.0008 . Weg. I ------- TABLE 8 AIR POLLUTANT EMISSIONS FROM BURNING OF FUELS BY STATIONARY SOURCES IN PROVIDENCE oiUL/i niu.'ij I yu / \ i uno/ iu/-m/ Source Industrial Natural Gas Fuel Oil Coal Residential Natural Gas Fuel Oil Coal Commercial Natural Gas Fuel Gas Coal Utilities Natural Gas Fuel Oil Coal * * Grand Total * Sulfur Oxides 19,200 Meg. * 19,000 200 24,900 Neg. 23,900 1,000 4,900 Neg. 4,900 .._ 67,100 . _- r-; ! 42,300 ''- 24,800 116,100 Parti c- ulates 2,050 40 1,400 610 1,790 180 560 950 240 40 200 ._ '10,400 1,200 '- 9,200 14,480 Carbon Monoxides 120 Neg. 100 20 2,040 Meg. 140 1,900 30 Neg. 30 ,*< 400 '\ \ Neg, -' 400 2,590 Hydro- carbons 100 Neg, 100 Neg. 590 Neg. 210 380 30 Neg. 30 560 ii' '"> 380 -' 180 1,280 Nitrogen Oxi des 5,540 300 5,100 140 1,250 1,100 850 300 1,260 260 1,000 * * 29,000 12,500 :" 16,500 37,050 *Neg. - Negligible -23 - ------- TABLE 9 NUMBER OF VEHICLE MILES TRAVELED IN PROVIDENCE STUDY AREA BY POLITICAL JURISDICTION, 1967 (Velnclc-Miles/Day) Providence Pawtucket SMSA Rhode Island Portion Barri ngton Bristol Burrniiville Central Falls Coventry Cranston Cumberland East Greenwich . East Providence Jamestown Johnston Lincoln Marragansett North Kingstown ; North Providence North Smith-field . Pawtucket Providence Smith-field Warren Warwick l/est Warwick Wconsocket Gasoline Powered 10,063,000 8,473,000 166,000 166,000 142,000 34,000 329,000 779,000 410,000 259,000 561,000 40,000 321,000 280,000 134,000 321 ,000 231 ,000 231 ,000 512,000. 1,450,000 197,000 118,000 1,352,000 212,000 228,000 Diesel Powered 129,000 110,000 2,000 3,000 2,000 Meg. 4,000 .11,000 5,000 3,000 7,000 Meg. . . 4,000 . 3,000 1 ,000 . 4,000 3,000 3,000 7,000 20,000 2,000 1 ,000 19,000 3,000 3,000 ------- TABLE 9 NUMBER OF VEHICLE MILES TRAVELED IN PROVIDENCE STUDY AREA BY POLITICAL JURISDICTION, 1967 (Vehicle-Miles/Day) Massachusetts Portion Attleboro Bellingham Blackstone Franklin Mill vllle North Attleborough Plainville Rehoboth Seekonk Wrentham Fall River SMSA Massachusetts Portion Fall River Somerset Swansea Westport Rhode Island Portion Tivertown New Bedford SMSA Acushnett Dartmouth Gasoline Powered 1,590,000 330,000 167,000 141,000 183,000 44,000 183,000 141,000 141,000 212,000 47,000 1,181,000 1,026,000 516,000 - . 160,000 . 167,000 183 ,.000 155,000 .155.000 1,068,000 47,000 209,000 Diesel Powered 19,000 4,000 2,000 2,000 2,000 Neg. 2,000 2,000 2,000 3,000 Neg. 15,000 ' 13,000 7,000 2,000 2,000 2,000 2,000 2,000, 0 11,000 Neg. 2,000 - 25 - ------- TABLE 9 NUMBER OF VEHICLE MILES TRAVELED IN PROVIDENCE STUDY AREA BY POLITICAL JURISDICTION, 1967 (Vehicle-Miles/Day) Falrhaven New Bedford Marion Mattapoisett Extra Rhode Island Towns Jamestown Middle town Newport Portsmouth Gasoline Powered 139,000 573,000 57,000 43,000 642,000 40,000 .180,000 158,000 264,000 Diesel Powered 1,000 8,000 Neg. Neg. 7,000 Neg. 2,000 2,000 3,000 Grand Total 12,954,000 162,000 ------- TABLE 10 GASOLINE AND DIESEL FUEL CONSUMPTION IN STUDY AREA BY SMSA, 1967 (106 cjal./year) Gasoline Consumption Evaporation Diesel Consumption Providence New Bedford Fall Fiver Total 294 31 34 359 ' 7 1. 1 9 9 0.5 1 10.5 - 27 - ------- TABLE Ti-A AIR TRAFFIC ACTIVITY AT THEODORE FRANCIS GREEN STATE AIRPORT, WARWICK, RHODE ISLAND CALENDAR YEAR, 1967 Air Carrier General Aviation Military Total Itinerant Operations 42,042 152,409 1 ,476 170,326 Local Operation --- 167,693 610 168,303 TABLE 11-B AIR TRAFFIC ACTIVITY AT NEW BEDFORD AIRPORT ,' NEW BEDFORD MASSACHUSETTS CALENDAR YEAR, 1967 Itinerant Local Operations Operations .Air Carrier 3,818 General Aviation 35,389 15,966 Military 1,958 5,238 Total : 41,165 . 21,204 - 28 - ------- TAOLE 12 AIR POLLUTANT EMISSIONS FROM TRANSPORTATION SOURCES IN PROVIDENCE STUDY AREA, 1967 (Tons/Year) Road Vehicles Gasoline Diesel Aircraft Jet Piston Railroad Totals Sulfur Oxides 1,680 1,420 260 Neg. Meg. . Neg. . 830 2,510 Parti cu- lates 2,620 1,900 720 - 100 10 90 50 2,770 Carbon Monoxides 407,900 407,500 400 7,640 7,110 530 Keg . 415,540 Hydro- carbons 31 ,300 30,400 . ": 900 1,560 510 1,050 Meg. 32,860 Nitrogen Oxidns 21,600 20,100 1,500 430 250 180 170 ' 22,200 - 29 - ------- FABLE 13 REFUSE BALANCE FOR-PROVIDENCE STUDY AREA, 1967 (Tons/Year) Jurisdiction Providence Pav; tucket SMSA Rhode Island Portion Harrington Bristol Durrilliville 1 Cc-ntral Fulls CO ^ Coventry^ . Cranston Cur,ibc-'rl and East Greenwich East Providence Jaraastown Johnston Lir.coln ttarragansett North Kingstown Total Refuse 715,150 623,700 13,500 . 13,100 8,000 ; 15,500 14,600 59,800 19,800 6,800 35,200 2,100 16,200 ' . 12,100 . 4,200 19,100 Incineration Municipal On-site Landfills 132,000 40,000 174,800 132,000 40,000 138,800 7,000 8,000 30,000 - 30,000 3,300 20,000 'lO.OQO Open ' On-site Dumps Burning 103,900 261,400 82,000 227,900 6,500 4,000 9,100 4,000 4,000 8,500 6,600 29,800 11,800 3,500 1,000 14,200 500 1,700 6,200 4,100 4,200 11,000 8,100 Transferred -7,000 +22,000 -8,000 ------- TABLE 13 REFUSE BALANCE FOR PROVIDENCE STUDY AREA, 1967 (Tons/Year) Jurisdiction North Providence ' f'orth Smithfield Pc'.wt'jcket Providence Smithfield Warren to "* l/arwick i .Host Warwick V'oonsocket Massachusetts Portion Attleboro ' Bellirighsm Blacks tone Franklin Mill ville North AUleborough Plainville Total . Incineration Refuse Municipal On-site Landfills Dumps 17,600 7,200 64,200 45,000 155,000 62,000 9,900 .8,100 64,500 18,200 39,000 25,000 91,400 ' 24,900 10,000 5,300 13,400 1,400 13,100 3,700 12,000 10,000 ' . 7,000 20,000 15,000 5,000 3,500 2,500 10,000 30,000 11,000 6,000 36,000 21,900 17,500 6,000 3,200 8,100 800 8,200 2,500 Open On-sita Burning 5,000 4,200 9,200 31 ,000 6,400 5,600 24,000 7,200 19,000 33,500 7,400 4,000 .2,100 5,300 600 4,900 1,200 Transferred -3,000 +7,000 -22,000 +11,000 ------- TABLE 13 REFUSE BALANCE FOR PROVIDENCE STUDY AREA, (Tons/Year) Jurisdiction Rshoboth Seekonk Wren th am Fall River. SMSA Massachusetts - Portion Fall River Somerset Swansea' He st port Rhode Island Portion liver town flew Bedford SMSA Acushnet Dartsnouth Total Refuse 4,600 8,600 6,400 124,500 115,300 84,500 13,400 10,200 7,200 9,200 9,200 121,200 5,800 14,500 Incineration Municipal On-site Landfills Dumps 2,700 5,100 3,800 15,000. 2,000 65,200 4,300 15,000 2,000 59,200 4,300 15,000 2,000 45,000 8,100 6,100 4,300 6,000 .6,000 20,000 13,100 55,800 ' 3,500 8,700 Open On-site- Burning Transferred 1,900 3,500 .. 2,600 '. 38,000 34,300 22,500 5,300 4,100 2,900 3,200 3,200 32,300 2,300 - 5,800 ------- TABLE 13 REFUSE BALANCE FOR PROVIDENCE STUDY AREA, (Tons/Year) CO OJ Jurisdiction . Fairhaven Hew Bedford Marion Mattapoisett Other Massachusetts Towns . Jamestown i-Hddletown import Portsmouth Totals 1 Total Refuse 13,400 81 ,500 2,500 3,500 56,700 2,200 16,200 29,500 8,800 ,017,500 Incineration Municipal On-site Landfills 8,100 20,000 1,500 21,000 19,000 13,000 21,000 6,000 188,000 42,000 272,100 Dumps 45,000 2,100 5,500 500 5,000 ' .165,500 Open On-site Burning Transferred 5,300 15,500 1 ,000 I -1,400 12,200 1,700 3,200 ^4,500 2,800 345,900 ------- TABLE 14 AIR POLLUTANT EMISSIONS FROM SOLID WASTE DISPOSAL IN PROVIDENCE STUDY AREA (Tons/Year) Total Incineration Municipal On- site Total Open Burning Dumps On-site Total SOX 230 190 40 Meg. * - Neg. Neg. 230 PART. 1,800 1,600 200 3,430 680 2? 750 5,230 CO . . 1,000 100 900 18,200 3,600 14,600 19,200 HC 50 30 20 1,100 220 880 1,150 NOX 250 190 60 2,360 470 .. 1 ,890 2,610 Neg. '-.- Negligible ', ' **-o' ,i .r.vv . - 34 - ------- ; METHODOLOGY The follov/ing discussion is a summary of procedures employed in Providence, New Bedford, Fall River emission inventory. Fuel Combustion by Stationary Sources The state air pollution agencies were contacted as to the use of fossil fuels in the major industrial and commercial establishments. Approximately 100 major industries and commercial establishments were located and their fuel consumption totaled. This amounted to approxi- mately 350 million gallons of fuel oil, one billion cubic feet of natural gas and 1.6 thousand tons of coal. The large industrial and conraercial facilities consumed most of the fuel oil and natural gas and the power plants used coal and fuel oil. On the basis of this infor- mation, 70 percent of the fuel oil and 96 percent of the coal-burned in the area was accounted for by point sources. The balance of the fuel burned in the Study Area was distributed to three area source categories of fuel consumption: (1) residential, (2) commercial-institutional and (3) industry. The amount of fuel burned for home heating was calculated using the procedure described in the "Rapid Survey Technique". The method includes such variables as total annual and winter degree days, average nitiTiber of rooms per dwelling unit, and the number of dwelling units using each fuel. It was assumed that all fuel oil burned for home heating was distillate. Commercial-Institutional fuel consumption figures were not avail- able except in the case of natural gas where the gas companies had sup- plied their figures. Natural gas for commercial establishments was found to be about from one fourth to one sixth of the amount sold to residential users. Fuel oil was determined by point sources and other reports already completed. It was assumed the coal consumption would be negligible for this category. - 35 - ------- After the approximate fuel consumption was determined all point sources, residential and commercial figures were subtracted from the total. The remainder was considered industrial and dis- tributed to thosa areas in the Study Area considered industrialized. Transportation Sources Transportation information was obtained from two major sources: (1) the State Highway Department of Massachusetts, and (2) the State Highway Department of Rhode Island. The State of Rhode Island had reliable information on the number of vehicle miles driven in all cities and towns in Rhode Island. The State of Massachusetts had a transportation study of Southeastern Massachusetts that gave vehicle miles for most towns in the Area, The remaining Massachusetts towns were estimated by population. Refuse Disposal Solid v/aste information v/as supplied by both Health Departments which had surveyed most of the dumps, landfills and incinerators in /'-. - :-, . . .' ' rt ..-.. v . . . .-. -. the Area. With this Information and approximate amount of refuse being generated in the area, a refuse balance was generated. That part of the solid waste being disposed of by open burning v/as distributed through the Study Area by population. Industrial Process Emissions The information used to estimate the process emissions from point sources v/as gathered by the acknowledged air pollution agencies. This data was most often in the form of production figures because actual process emissions, for the most part, were not available. - 36 - _ ------- 4,620,°°° 4,620,°°° 4,610,0°° 4,600,°°° Pov,-er Plants Incinerators Airports Industry Figure 3. Point source locations in the Providence- i:, firji; Dodforci, and Fall River 5ic;i,.iy Area - 37.- ------- . I- MASSACHUSETTS / | /_ Y "v~7 miles Figi.-re 1. Providsnce-Pavvtucket, Fall River and New Bedford Study Area. . ------- 290, 270 000 230,00° y % 320,000 4,650,00° 600 000 Figure 2. Grid system of Providence study area. ------- V / 290,°°° 300,°°° 310,°°° 4.670, 330,00° 340,000 350,°°° 360,000 0.04 - 0.10 0.10 - 0.50 Figure 4. Sulfur oxide emission density map for Providence study area. ------- 290,000 300,000 270i000 280,00° r.-rr~ ».. 310,000 4,670,°°° , 4,660,000 o; 320,000 4,650,°°° 330,000 , 340,000 350,000 360, °00 ^'iliililiilil ii"" /^KSillf Plillv, ^.iil ~\ >1.00 Figure 5- Particulate emission density map for Providence study area. ------- C30 MM 1-75 - 5.0 E&U&IJ&H >5.00 Figure 6. Ca.'bon monoxide emission density map for Providence study area. ------- 2/0,000 280, °°° :i;S::i;|S:.j 0.10 - 0.25 m °-25 - °-75 r"-~"i >0.75 Figure 7. Hydrocarbon emission density map for Providence study area. ------- 340,000 350,000 360. COO I -J~ 0.03 - 0.10 lilll 0.10 _ 0.50 iiiiiiiil pSl 0.50 - 1.00 iiiiv^AJ r1 >i.oo F,gurc 8. Nitrogen oxide e.is.ion d.n.1., n«P .or Providonca siudy area. ------- TABLE SUMMARY OF AREA SOURCE EMISSIONS FOR PROVIDENCE, NEW BEDFORD & FALL RIVER STUDY AREA, 1967.(TONS/DAY) Grid 1 2 3 4. 5 6 . 7 8 9 10 11 12 13 H 15 16 17 Hor, Coor. . (100m) . 2750 .2850 . .2950 '. 3050 2750 2850 2950 3050 3150 2850 2925 2975 3025 3075 2925 2975 3025 Vert. Coor. (100m) 46550 46550 46550 46550 46450 46450 45450 46450 ' 46450 46350 46375 46375 45375 46375 46325 . 46325 4C325 Area (sq mi) 38.60 30.60 38.60 38,60 38.60 33.60 33.60 . 33.60 38.60 33.60 9.65 9.65 9.65 9.65 9.65 9.65 9.65 SUM. 0.00 .10 .19 .12 .05 .06 .21 .40 .16 .21 ..06 6.64 7.01 .07 . .04 7.35 6.64 SOX 'WIN. 0.00 .23 2.67. .87 .44 .40 1.21 2.98 .45 1.29 .59 8.62 11.75 .68 .40 13.98 8.72 AVG. 0.00 .16 1.50 .48" .26 .23 .70 .1.80 .32 .77 .30 7.60 9.70 .38 .21 10.86 7.75 SUM. 0.00 .06 .78 .30 .15 .16 .51 .68 .10 ,11 .40 1.03 1.35 .25 .22 1.52 .96 PART. WIN. 0.00 .18 1.36 .47 .22 .23 .64 1.23 .12 .19 .53 1.55 3.06 . .35 .35 3.07 1.55 AVG. 0.00 .17 1.27 .38 .19 .19 .57 .94 .10 .15 . .46 1.27 2.10 .29. .30 3.27 1.25 SUM. /- f .57 15.45 41.12 28.19 11.92 14,03 37.04 49.44 7.03 7.80 15.00 38.86 70.95 16.50 11.88 92.95 46.06 CO WIN. .49 13.35 36 . 1 1 . 24.50, 10.35 12.18 32.08 44.11 6.09 '6,75 13,03 34.06 63.38 14.30 10.37 on oo Ou uo 40.42 AVG. ^53 14.33 38.51 26.22 11.07 13.02 "34.40 47.03 6.53 7.24 1 3, 97 35.35 65.74 15.32 11.07 86 . 96 43.01 ------- TABLE SUMMARY OF AREA SOURCE EMISSIONS FOR PROVIDENCE, NEW BEDFORD & FALL RIVER STUDY AREA, 1967 (TONS/DAY) Grid . IS 19 20 21 22 23 24 25 26 27 23 29 30 31 32 33 ; 34 35 36 37 Hor. Coor. (100m) 3075 3150 2850 2925 2975 3025 . 3075 2925 2975 3025 3075 3150 . 3250 3350 3450 2850 2950 3050 31.50 3225 Vert. Coor. (100m) 46325 46350 46250 46275 46275 46275 46275 46225 46225 46225 46225 46250 46250 46250 46250 '45150 46150 46150 46150 46175 Area (sq mi) 9.65 38.60 38.60 9.65. 9.65 9.65 9.65 9.65 9.65 9.65 9.65 38.60 38.60 38.60 38.60 38.60 38.60 38.60 38.60 9.65 SUM. .04 .06 .05 .04 6.79 6.70 .09 .07 .15 .11 .09 .15 1.27 .08 .01 .11 .52 .15 1.20 1.33 SO WIN. .38 .14 .34 - .41 10.33 9.07 .75 .66 1.42 .44 .69 1.45 3.25 ' 1.84 .33 .89 2.70 1.02 2.16 2.95 AVG. .21 .10 .19 '.22 8.58 7.86 .40 . .36 .77 .27 .38 ;82 2.25 .95 .17 .50 1.63 .58 1.76 2.14 . SUM. .12 .06 .14 .14 1.46 1.19 .25 .23 .49 ...26 .24 .46 .60 .46 .07 .26 .79 .37 .36 .33 PART. WIN. .22 .06 .18 .21 2.96 1.76 ..37 .33 .77 .35 .36 .71 .93 .73 .14 .36 1.30 .58 .61 .88 AVG. ..17. .06 .16 .17 1.98 1.47 .31 .28 .62 . .30 .30 .57 .75 .60 ' .10 .31 1.04 .47 .48 .58 SUM. 11.11 4.93 9.79 11.75 83.00 76.13 17.94 ]S083. 33.18 24.78 17.84 24.73 12.55 13.33 2.56 19.92 69.27 34.46 .20.94 21.90 CO WIN. 9,70 4.30 8.47 10.21 70.90 65.31 V5.64 16.34 23.95 21,53 15.50 21.59 10.95 11.91 2.23 17.32 60.29 29,95 18.37 19.43 AVG. 10.36 4.62 9.09 10.93 75.55 70.86 16.70 17.49 30.92 23.04 16.59 23.05 13.64 12.64 2.40 18.32 64.46 32.05 19.56 20.64 ------- TABLE SUMMARY OF AREA SOURCE EMISSIONS FOR PROVIDENCE, NEW BEDFORD & FALL RIVER STUDY AREA, 1967 (TONS/DAY) Grid 38 39 40 41 42 43 44 i 45 46 . 47 49 50 51 52 53 54 Hor. Coor. (100m) 3275 3325 .3375 3425 3475 3550 3550 3225 3275 3325 3375 3425 3475 2950 3050 3150 3250 Vert. Coor. (100m) 46175 46175 46175 46175 45175 46150 . 46250 46125 46125 46125 46125 46125 45125 46050 45050 ' 46050 45050 Area (sq mi) 9.65 9.65 9.65 9.65 9.65 33.60 38.60 9.65 9.65 9.65 9.64 9.65 9.65 38.60 38.60 38.60 38.60 SUN. .05 .05 .10 .03 0.00 .03 0.00 .02 .02 .05 1.43 1.59 .01 .07 .02 .12 .01 SO WIN. .67 .50 2.03' .48 .74 1.75 .46 .14 .12 .36 2.89 2.61 .35 .54 .28 .77 .19 AVG. .35 .27 1.06 .25V .37 .88 .23 ' .08 .07 .20 2.35 2.11 .18 .31 .15 . .46 .10 SUM. .14 .33 .40 .10 .17 .28 .07 .05 .05 .14 .49 ,.28 .07 .21 .09 .27 .05 PART. WIN. .' .27 .40 . .83 .21 .29 .66 .15 .05 .05 .17 1.26 .61 .13 .27 .14 .49 .07 AVG. .21 .37 .61 ..16. .33 .46 .11 -.05 .05 .16 . .86 ' .34 .10 .24 .12 .38 .06 SUM. 8.16 10.37 19:29 8.03 1.65 4.76 1.56 5.57 5.77 .9.35 . 31.03 13.34 2.44' 14.43 6.86 28.60 2.34 CO VII H. 7.19. 9,13. 16.13 6.95 1.59 4.53 1.40 - 4.80 4'. 93 8.10 27.56 11.76 .2.15 12.50 5.95 24.74 2.04 AVG. 7 '.5 3 9.71 17.12 7.50 1.61 4.63 1.47 5.16 5.35 8.68 29.11 12.14 2. 23 13.39 6. '37 26.55 2.18 ------- TABLE SUMMARY OF AREA SOURCE EMISSIONS FOR PROVIDENCE, NEW BEDFORD & FALL RIVER STUDY AREA, 1967 (TONS/DAY) Grid 55 56 57 58 59 60 61 62 Hor. Coor. (100m) 3350 3450 3950 . 3050 3150 2950 2950 3050 Vert. Coor. (100m) 46050 46050 45950 45950 45950 45850 46G50 46650 Area (sq mi) 38.60 38.50 38.60 38.60 38.60 38.60 30,60 38.60 SUM. 1.21 14 .02 .14 .02 .38 .06 .04 SOX .WIN. 1.33 .67 .07 2.52 .40 .54 .36 .42 AVG. '1.30 .45 .04 1.3T .21 .48 .20 .23 SUM. .15 .08 .01 .43 .09 .11 .17 .14 PART. WIN. .18 .11 . .05 .92 .18 .13 .21 .19 AVG. .16 .09 .01 .67 .13 .12 .18 .17 SUM, 7.67 5.24 2.46 27.36 6.78 8.50 12.63 10.31 CO WIN. 6.62 4.54 2,75 24.06 . 5.96 7.33 10.99 8.94 AVG. 7.10 4.86 2.30 24.14 6.34 7.88 11.78 9.57 ------- TABLE 15 SUMMARY OF EMISSIONS'FROM.POINT'SOURCES IN PROVIDENCE, NEW BEDFORD, AND FALL RIVER STUDY AREA, '1967 (TONS/DAY) OJ CO Source Category Incinerator Incinerator Incinerator Incinerator Incinerator Airport Ai rport Industry Industry Industry Industry Industry Industry industry Industry Institute, n Institution Industry Institutrm Industry Industry Grid 12 23 3 36 43 40 26 3 3 :- 2 : : 1.1 "f 8 8 9 12 . 12 13 13 13 14 Her. Ccor. (100m) 2993 3015 2932 3173 3370 3370 2975 2925 2926 2880 2936 2936 3004 3070 3115 2978 2954 3021 3005 3003 3051 Vert. Coor. (100m) 45373 46297 46523 4G170 46143 46155. 46220 45539 46534 46600 46378 46458 46403 46408 46452 46352 45359 46376 46357 ' 46369 46394 SUM. 0.12 0.17 0.07 0.04 0.05 . 0. 00 . 0.00 0.09 0.17 0.00 0.00 1.86 2.58 4.70 1.24 .0.00 0.05 1.12 0.10 0.16 0.27 SOX WIN. 0.12 0.17 0.07 0.04 . 0.05 .0.00 .0.00 0.63 0.57 "2.05 0.68 2.59 2.80 5.52 1.73 0.81 0.70 1.12 0.60 0.54 0.56 AVG. 0.12 - 0.17 0.07 0.04 0.05 0.00 0.00 0.44 0.43 1.30 0.32. 2.33\ 2.72. 5.22 1.55 0.5T 0.46 1.10 0.34 0.40 0.45 - SUM. 1.05 .1.44 0.58 0.35 0.47 0.02 0.25 0.01 0.01 0.00 0.00 0.13 0.17 .0.31 0.08 0.00 0.00 0.03 0.01 0.01 0.02 PART. - WIN. 1.05 1.44 0.53 0.35 0..47 0.02 -.' 0.25 0.04 0.04 0.13 0.05 0.18 0.18 0.36 0.11 0.05 0.05 0.03 0.04 0.04 0.04 AVG. 1.05 1.44 0.58 . 0.35 0.47 0.02 0.25 0.03 . 0.03 0.09 0.02 '0.16 0.18 0.34 0,10 0.03 0.03 0.03 0.02 0.03 0.03 SUM. 0.06' 0.08 ' 0.03 0.02 0.02 4.37 16.55 0.00 0.00 0.00 0.00 0.01 0.01 0.03 0.01 0.00 0.00 0.00 0.00 0.00 0.00 CO WIN. 0.06 0.08 0.03 0.02 0.02 4.37 16.55 0.00 0.00 0.01 0.00 0.01 0.02 0.03 0.01 0.00 0.00 0.00 0.00 0.00 0.00 AVG. 0.06 0.08 0.03 0.02 0.02 4.37 16.55 0.00 0.00 0.01 0.00 0.01 0.02 0.03 0.01 0.00 0.00 0.00 0.00 0.00 0.00 SUM. 0.02 0.03 0.01 0.01 0.01 0.81 3.44 0.00 o.oo 0.00 0.00 0.01 0.01 0.03 0.01 0.00 0.00 0.01 0.00 0.00 0.00 HC WIN. 0.02 0.03 0.01 0.01 0.01 0.81 3.44 0.00 0.00 0.01 . 0.00 0.01 0.02 0.03 0.01 0.00 0.00 0.01 0.00 0.00 0.00 AVG. 0.02 0.03 0.01 0.01 0.01 0.81 3.44 0.00 0.00 0.01 0.00 0.01 0.02 0.03 0.01 0.00 0.00 0.01 O.GO 0.00 0.00 SUM. 0.12 0.17 0.07 0.04 0.05 0.21 .97 0.02 0.04 . 0.00 0.00 0.43 0.53 0.97 0.26 0.00 O.OT 0.33 0.02 0.03 0.06 NOX WIN. AV 0.1 '2 0. 0. 17 0. 0.07 0. 0.04 0. 0.05 0. 0.21 0. .97 . 0.13 0. 0.12 0. 0.52 0. 0.14.0. 0.60 0. 0.58 0. 1.14 1. 6.36 0. 0.17 0. 0.14 0. 0.33 0. 0.12 0. 0.11 0. 0.11 0. ------- TAELE 15 SUMWW OF EMISSIONS FROM POINT SOURCES IN'PROVIDENCE, HEa BEDFORD, AMD FALL RIVER STUDY AREA, 1967 (TONS/DAY) Source Ca';^Qory Grid Industry Industry '.'Institution Fov.-cr Plant Institution . Industry ... Industry Industry Industry -o Industry > Industry , Industry : Industry '. Pov/er Plont Pov/er Plant Industry Industry Industry Industry Pov.'er Plant 16 15 i *~ !0 16 17 :17 22 22 22 25 . ?-6 26 23 3D 30 36 -i ' OU ,-» Q . 40 ' 48 ilor. Cocr. (IGCfii) 2975 2997 ^^ ^>.n tL-j-sa 2993 3002 3213 2903 2938 2992 2980 29'66 2950 3050 3205 3215 3195 3112 3397 3395 1 i 3390 V.prf, Ccor. (in(fci) 46306 46317 46314 46323 45329 46167 46275 46276 46298 46209 46221 46222 46290 46202 46230 46185 46155 46085 46120 46100 SUM. 0.7ft 0,36 0.67 43.96 0.74 0.48 .-^ 0.41 0.32 0.21 0.31 1.45 7.55 0.84 62.18 0.94 0.71 0.54 n.03 16.07 SOy WIN. 1.03 O.F1 2.11 48.96 0.74 1.40 0.93 0.58 0.65 0.71 0.64 1.71 7.55 0.84 62.18 1.10 1.63 .0.76 0.59 16.07 AVG. . 0.97 0.45 1.35 48.96 0.74 1.06 . 0.90 0.52 0.53 0.53 0.52 1.62 7.55 0.84 62.18 1.04 1.29 0.68 0.41 16.07 'SUM. ' 0.06 0.02 0.04 2.10 0.03 0.03 1. CO 0.03 0.02 0.01 0.02 0.10 0.50 ;0.02 1.73 0.06 0.05 '0.04 0.01 0.46 PART. WIN. 0.09 0,03 0014 2.10 0.03 0.09. 1.80 0.04 0.04 0.05 0.04 o.n 0.50 0.02 1.78 0.07 0.11 0.05 0.04 0.46 AVG. 0.08 0.03 0.09 2.10 0.03 0.07 1.80 0.04 0.03 0.03 0.03 0.11 0.50 0.02 0.07- 0.08 0.04 0.03 0.46 OHM bbi'l. 0.00 0.00 0.00 0.12 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.01 0.04 0.00 0.01 -0.01 0.00 0.00 0.00 0.00 CO WIN. 0.01 0.00 0.01 0.12 0.00 0.01 0.01 0.00 0.00 0.00 0.00 0.01 0.04 0.00 0.01 0.01 0.01 0.00 0.00 0.00 AVG. 0.01 0.00 0.01 0.12 0.00 0.01 0.01 0.00 0.00 0.00 0.00 0.01 0.04 0.00 0.01 0.01 : 0.01 0.00 0.00 0.00 SUM. o.oo o.oo 0.00' 0.38 0.01 0.00 0.00 0.00 0.00 0.00 0.00 0.01 0.04 0.01 0 57 0.01 O.GO 0.00 0.00 0.15 HC WIN. 0.01 0.00 0.01 0.33 0.01 0.01 0.01 0.00 0.00 0.00 0.00 0.01 0.04 0.01 0.57 0.01 0.01 0.00 0.00 0.15 AVG. 0.01 0.00 0.01 0.33 0.01 0.01 0.01 0.00 0.00 0.00 o.co 0.01 0.04 0.01 0.57 0.01 0.01 0.00 0.00 0.15 MOX SUM. HIM. AVG. 0.28 0.40 0.35 0.03 0.11 0.09 0.14 0.43 0.28^ 15.2515.25 15.25 0.32 0.32 0.32 0.10 0.29 0.22 0.18 0.20 0.19 0.14 0.19 0.17 0.07 0.13 0.11 0.04 0.15 0.11 0.06 0.13 0.11 0.30 0.35 0.33 1.57 1.57 1.57 0.25 0.25 0.25 18.49 18.49 18.49 0.20 0.23 0.22 0.15 0.33 0.27 0 11 . 0.16 0.14 0.02 0.12 O.OS 4.78 4.78 4.7F ------- TABLE 15 SUMMARY OF'.EMISSIONS FROM POINT SOURCES IN PROVIDENCE, NEW BEDFORD, AND FALL RIVER STUDY AREA, 1967 (TONS/DAY) Source Cdt-^'iory Industry Industry Power Plant 'Power Plant /"* s,, ^ j bl 1 U 49 .49 37 58 iicr. Coor. ( "i OGm ) 3400 3400 3173 30SO Vert. Ccor. (lOOni) 45146 46150 45200 45960 SUM. 0.66 .0.31 53.20 2.55 sox Hill - 0.84 - 0.80 53.20 .2.55 AV6. 0.78 0.63 53.20 2.55 . SUM. 0.04 0.02 24.00 0.07 PART. WIN. 0.06 0.05 24.00 0.07 AVG. 0.05 0.04 24.00 ' 0.07 SUM. 0.00 0.00 1,00 0.00 CO WIN. 0.00 0.00 1.00 0.00 AVG. 0.00 0.00 1.00 0.00 SUM. 0.00 o.oo 0.40 0.02 HC WIN. 0.00 0.00 0.40 0.0? AVG. 0.00 . 0.00 0.40 0.02 SUM. 0.14 0.07 40.00 0.75 NOX ,Mlfl. 0.17 0.07 40.00 0.75 AVG O.lr 0.1: 40. Of 0.7* ------- TABLE 16 SUMMARY OF TOTAL SOURCE EMISSIONS BY GRID FOR PROVIDENCE, NEW BEDFORD, ft FALL RIVER STUDY AREA 1967 (TONS/DAY) Grid 1 2 3 4 '-' 6 / i 1 a o 7io c 11 12 < 13 14 { y 16 17 13 '19 Hor. Coor. (ICCm) 2750 2850 2950 3050 2750 2850. .. 2950 . 3G50 3150 2850 2925 2975 3325 - 2075 2325 2375 3025 3075 2150 Vert. Coor. (100.0 46550 4C5DO 46550 ^5550 . 4G450 46450 15450 45450 46450 45350 4G375 45375 4C375 45375 45325 4G325 46325 45325 46350 Area (sq mi) 33.60 38.60 38.60 33.60 . 3G.60 38.60 38.60 33.60 33.60 38.60 9.65 9.65 9.65 9.65 9.65 9.65 9.65 9.65 38.60 SUM. 0.00 .10 .52 _: .12 .05 .06 2.07 7.58 1.40 .21 .06 6,81 8.49 .34 .04 58.12 7.88 .04 .06 SOX WIN. 0.00 2.28 3. 94 .87 .44 .40 3.80 1 1 . 30 2.18 1.29 1.27 10.25- 14.01 1.24 .40 66.64 10.86 .38 .14 AVG. 0.00 1.46 2.44 .48 .26 .23 3.03 9.74 1.37 .77 ,64 8.69 11.54 .83 .- .21 62.83 9.55 .21 .10 SUM. 0.00 .06 1.38 .30 .15 .16 .64 1.16 .18 .11 .40 1.03 1.40 .27 .22 3.74 .1.02 .12 .06 PART. WIN. 0.00 .31 2.02 . .47 .22 i .23 .82 1.77 .23 .19 .58 2.70 3.27 .39 .35 5.43 1.67 .22 .06 AVG. 0.00 .26 1.91 .33 .19 .19 .73 1.45 .20 .15 .48 2.38 2.18 .32 .30 5.57 1.35 .17 .06 .SUM. -.57 15.45 41.15 28.19 11.92 14.03 37.05 49.48 7.04 7.80 15.00 38092 70.95 16.50 11.83 93.07 46,05 11.11 4.93 CO WIN. .49 13.36 36.14 24.50 10.35 12.18 32.09 44.15 6.10 6.75 13.08 34.12 63.38 14.30' 10.37 81.01 40.43 9.70 4.30 AVG. 0.53 .- 14.34 38.54 26.22 11.07 13.02 34.41 47.08 6.54 7.24 13.97 36.41 66.74 15.32 11.07 87.09 43.02 10.36 4.62 SUM. ' 0.07 2.12 4.11 3.56 1.61 1.91 5.41 6.35 .96 1.13 1.33 5,25 7.61 2.06 1.50 10.27 5.10 1.39 .73 HC WIN. 0.06" 1.R4 4.59 3.13 1.41 1.69 4.71 5.65 .84 .98 1.65 4.75 7.08 1.81 1.31 9.39 4.59 1.22 .63 AVG. 0.07 1.97 4.82 3.32 1.50 1.78 5.04 5.97 .89 1.05 1.75 4.93 7.29 1.93 1.40 '3.79 *,S2 1.30 .63 SUM. 0.03 1.01 2.57 1 . 60 .78 .90 3.17 4.51 ' .76 .6?. .85 3.7C. 4.35 1.06 .60 21.01 3.6- .6: . 3J NOX WIN. 0.04 1.50 3.75 1.69 . .87 .93 3,49 '5.30 .92 .83 liar 4.64 5.98 1.06 .70 22.93 4.28 .66 .33 0 1 3 1 - 3 4 4 5 1 21 ;- ------- TABLE 16 SUMMARY OF TOTAL SOURCE EMISSIONS BY GRID FOR PROVIDENCE, HEM BEDFORD & FALL RIVER STUDY AREA ' 1967 (TONS/DAY) Grid 20 21 22 23 24 25 26 27 23 29 C30 -31 ' t_ 33 34 35 36 37 Hor. Co or. (100m) 2350 2925 2975 3025 3075 2925 2975 3025 3075 3150 3250 3350 3450 2350 2950 3050 3150 3225 Vert. Coor. .(lOOn) 46250 45275 46275 46275 - 46275 45225 46225 .46/25 45225 46250 45250 462 50 46250 461 50 46150 46150 46150 46175 Area' (sq mi) 33.60 9.65 9.65 9.55 9.65 9.65 9.65 9.65 9.65 38.60 38.69 ,38.60 .33.60 38.60 *3 o r A 38.60 38.60 9.65 SUM. .05 .04 3.33 6.78 .09 .07 2.13 .11 7.64 .15 64.29 .08 .01 . .11 .52 .15 2_.39 54.53 SOX WIN. .34 .41 12.54 . 9.24. .75 .66 . 4.43 .44 8.24 1.45 66.27 1.84 .33 .89 2.70 1.02 4.93 56.13 AVG. .19 .22 10.53 8.03 .40 .36 3.44 .27 7.93. .32 65.27 '.95 -17 .50 1.63 . 58 . 4.13 55.34 SUM. .14 .14 3.31 2.53 ..25 .23 .37 .26 .74 .46 2.40 .45 .07 .26 ' .79 .37 .82 24.33 PART. WIN. .18 .21 . 4.84 3.20 .37 . .33 1.22 .35 .86 .71 2.73 .73 .14 .36 1.30 .58 1.14 2^,88 AVG. i .15 .17 3-. 85 2.91 .31 .28 1.04 .30 .80 .57 2.55 .60 .10 .31 1.04 .47 .98 24.58 SUM. 9.79 11.75 83.00 76.21 17.94 18.83 49.74 24.78 17.84 24.73 12.56 13.33 2.56 19.92 69.27 34.46 . 20.97 22.90 CO WIN. 8.47 10.21 70.91 65,39' ' 15.64 16.34 45.51 21.53 15.54 21.59 10.96 11.91 2.28 17.32 60.29 29.95 18.41 20.43 AVG. 9.09 10.93 75.56 70.94 16.70 17.49 47.48 23.04 16.63 23.05 13.65 12.64 2.40 18.52 64.46 32.05 19.60 21.64 SUM. 1.42 1.47 9.87 8.21 2.43 2.36 7.61 3.12 2.46 ' 3.59 2.60 1.50 .35 2.91 8.74 4.35 2.71 3.27 HC 'WIN. 1.24 1.33 8.'. 35 7 . 31 2.12 2.06 7.12 2.72 2,17 3.23 2.46 2.14 ' .32 2.55 7.63 3.81 2.35 2.94 AVG. 1.32 1.37 9.34 7.72 2.26 2.20 7.34 2.91 2.30 3.17 2,51 1.71 .33 2.72 8.17 4.06 2.57 3. 13 SUM. .72 .6;1. 5.S5 4.49 .1.20 1.06 3.31 1.40 2.75 1 . 84 20.23 1.09 .19 1.45 3.99 1.95 1.92 41.61 WIN. .74 .78 6.70 3.93 1.54 1.17 3.75 1.45 2.96 2.03 20.46 1.25 .27 1.54 4.26 2.22 2.29 42.21 AVG .7 .7 e:'2 4.7 -:.' 1.3 "1.1 3.5 1.4 2.3 1.9 20.3 1.1 <- 1.4 4.0 2.0 .1.8 41. t ------- ' TABLE 16 SUMMARY OF TOTAL SOURCE EMISSIONS BY GRID FOR PROVIDENCE, NEW BEDFORD & FALL RIVER STUDY AREA ' . - 1967 (TONS/DAY) Grid 33 39 40 41 42 43- 44 45 46 47 4.3 49 5'0 51 52 53 54 55 56 Kor. Coor. (100m) 3275 3325 3375 3425 2475 3550 3550 3225 3275 3^> *~*, f 4..-' b 3375 34^5 3475 2950 3050 31 GO 3250 3350 ' 3450 Vert. Coor. (lOOn) 46175 46175 4G175 46175 46175 45150 45:!50 46123 46125 46125 '46125 ' 46125 46125 46050 450^0 46050 45050 45050 46050 Area (sq mi) 9.65 9.65 9.65 9.65 9.65 38.60 38.60 9.65 9.65 9.65 9.65 9.65 9.65 38.60 38.60 38.60 38.60 38.60 33.60 sun. .05 .05-, .10 .03 0.00 .03 0.00 ' .02 .02 .05 18.12 2.56 .01 .07 .02 .12 .01 1.21 .14 WIN. .67 .50 2.03 .43 . .74. 1.75 .46 .14 .12 .36 20.31 4.25 .36 .54 .28 .77 '.19 1.33 .67 AVG. .35 .27 1.06 .25 .37 .88 .23 . .08. .07 ..20 . 19.41 3.52 .18 . .31 .15 .46 .10 1.30 . .46 SUM. .14 .33 .42 .10 .17 .28 .07 .05 . .05 .14 1.00 .34 .07 .21 .09 .27 .05 .15 .08 PART. WIN. .27 .40 .85 .21 .29 .66 .15 .05 .05 .17 1.81 . .72 .13 .27 ' .14 .49 .07 .18 .11 AVG. .21 .37 .63 .16 .33 .46. .11 .05 .06 .16 1.39 .43 .10 .24 .12 .38 .06 .16 .09 SUM. 3.16 10.37 23.56 8.03 1.65 . 4.76 1.56 5.57 5.77 9.35 31.03 13.34 2.44 14.43 6.86 28.60 2.34 7.67 5.24 CO WIN.' 7.19 9.13 20.50 6.95 1.59 4.53 1.40 4.80 . 4.98 8.10 27.56 11.76 2.15 12.50 5.95 24.74 2.04 6.62 4.54 AVG. . 7.53 9.7.1 21.49 7.50 1.61 4.63 1.47 .5.16 5.35 .; -8.63 ' 29.11 12.14 2.23 13.39 6,37 26.55 2.18 7.10 4.86 ' SUM. 1.17 1.41 3.36 1.02 .17 '.59 .19 .75 .79 1.35 4.03 1.53 .31 2.10 .85 3.62 .32 1,13 .70 HC WIN. T.05 1.24 3.13 .90 ."9 .63 .19 .65 .68 1.17 4.31 . 1.47 .30 1.81 .74 3.16 .28 .86 .60 AVG. 1.11 1.31 3.23 .95 .13 . .61 .19 .70 .73 1.25 4.95 1.55 .30 1.95 .73 3.37 .30 1.03 .65 *;:M 1.12 .33 i . 56 .47 .16 .44 .14 .35 .37 » C 2 7.H l.rs . - O 1.7 . ' j l.TO .19 .73 . ': 3 N'0X WIN. 1.21 .89 1.91 .53 .28 1.10 .28 .33 .32 .68 8:10 1.74 .27 1,15 :44 1.63 .24 .81 .44 * AVG. 1.16 .85 1.75 .49 .22 .47 .20 .3". .3-1 .5C 7.60 1.58 .22 1.11 ' .41 1.6: .21 ..8.r: .41 ------- TABLE 16. SUMMARY OF TOTAL SOURCE EMISSIONS BY GRID FOR PROVIDENCE, NEW BEDFORD & FALL RIVER STUDY AREA 19G7 (TOMS/DAY) * - Grid 57 58 59 60 '61 62 Hor. Coor. (IQOnO 2950' 3050 3150 2930 2950 3050 Vert. Coor. OCCfo) 'GD50 .45950 45950 45850 4C650 4GC50 Area (sq mi) 38.60. ' 33.60'^ 38.60 33.60 33.60 38. CO SUM. .02 2.69 .02 .33 .06 .04 SOX WIN. .07 5.07 .40 .54 .36 .42 AVG. . .04 3.86 .21 . .43 .20 .23 SUM. .or .50 - ^09 .11 .17 .14 PART. WIN. .05 .99 .18 .13 .21 .19 AVG. '.01 .74 .13 ,12 .18 .17 SUM. 2.46 27.36 6.78 8.50 12,68 10.31 CO WIN. 2.15 24.06 5.96 7.33 10.99 8.94 AVG. 2.30 24.14 6.34 7.88 11.78 .9.57 SUM.. .30 3.10 .85 1.16 1.72 1.39 HC WIN. .27 2.84 .75 1.00 1.50 1.21 AVG. .23 2.96 .79 1.08 1.60 1.29 SUM. .14 2.15 .40 .61 .34 .63 NOX WIN. .14 -2.68 .47 , .64 .94 . .73 AVG. .l-'l 2.39 . -43 .62 °3 .70 ------- EMISSION DENSITIES BY GRID Emission densities on a grid basis v/ere obtained by summing the annual area and point source emissions for each grid. This total, divided by the grid area, gives an emission density in tons per square mile per average day. Figures 4 through 8 present the emission den- sity maps for the five surveyed pollutants. It is difficult to make any valid conclusions from the emission density maps alone. For this reason when they are analyzed, the detailed map of the Study Area and the point source location map should also be considered. -45- ------- REFERENCES 1. Ozolins, G, and Smith R,, Rapid Survey Technique for Estimating Community Air Pollutions, DMEH, PUS, October, 1966. 2, Duprev, R.L. Compilation of Air Pollution Emission Factors, OHEK', PHS, April 1967. " 3. Personal Communication with 'lassachusetts State Health Department, Air Use Manaoement. . 4. Personal. Communication v/ith R'iode Island Stats Donsrb'isnt of Health, 'Division cf Air Pollution Control. . \ * » - ^ 5, Fuels and Electric Energy Consumed in 'anufacturinn Industries-, - U.S. Dureau of Census, 1962, ; f 6. FAA Air Traffic Activity, Calender Year 1967, Department of Transportation, Federal Aviation Administration, February I960. 7. Personal Con:;-iunication v/ith Rhocig Island Highv/ay Cepartnient.- 8S Personal Coriniunicati-on with ,'lassachusctts Kighv/r.y Department. 0. Highv/ay Statistics/1965, M.S. Department of Transportation. -51- ------- |