Evaluation of the Atmospheric Deposition of Toxic Contaminants to Puget Sound: Appendices

EPA 910/9-91-027
Puget Sound Estuary Program
Evaluation of the
Atmospheric Deposition of
Toxic Contaminants to Puget Sound

Appendices
August 1991

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EPA 910/9-91-027
  ugef Sound Estuary Program
Evaluation of the
Atmospheric Deposition of
Toxic Contaminants to Puget Sound

Appendices
Prepared by:  Puget Sound Water Quality Authority
          Olympia, Washington

Prepared for:  U.S. EPA Region 10
          Seattle, Washington
          Project Number CE-000412
August 1991

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                          TABLE OF CONTENTS

                                                                        Page

A.   LITERATURE SURVEY	1
     Mass Balance  	1
     Great Lakes  	2
     Microlayer	3
     Sediments	4
     Stormwater Runoff	6
     PAHs and PCBs	7
     Modeling	8
     Miscellaneous  	9
     Puget Sound Summary	10

B.   METEOROLOGICAL DATA	  11
     B-l.   Hourly Meteorological Data  	  13
     B-2.   24-Hourly Meteorological Data  	  93
     B-3.   Air Stagnation Episodes	99
     B-4.   Data for Air Stagnation Analysis   	107

C.   LABORATORY RESULTS - SEX-MONTH AEROSOL AND DEPOSITION
     STUDY	115
     C-l.   Sampling and Analysis Protocols   	117
     C-2.   Sample Selection for Analysis  	119
     C-3.   Total Suspended Paniculate Data   	123
     C-4.   Elemental Aerosol Concentrations	135
     C-5.   Paniculate PAH Concentrations  	143
     C-6.   Vapor PAH Concentrations	153
     C-7.   Paniculate and Vapor Aliphatics and PCBs  	159
     C-8.   Deposition Metals  	165
     C-9.   Nutrient Data	171
     C-10. Concentrations of Aliphatic Hydrocarbons and PCB
           Congeners in Deposition Samples	177
     C-ll. PAH Deposition Data	181
     C-12. Quality Control for Chemical Analysis	189

D.   EMISSION INVENTORY	201
     D-l.   PSAPCA Point Source Metal and PAH Data  	203
     D-2.   Source Profile Information  	211
     D-3.   Kaiser Emission Data  	243
     D-4.   Simpson Tacoma Kraft Source Test	247
     D-5.   Area Source Emission Calculations	265

E.   LABORATORY RESULTS-18-DAY RECEPTOR MODELING
     FIELD STUDY	271
     E-l.   Ambient Monitoring for Receptor Modeling Study	273
     E-2.   Fine-Particle Results	279
     E-3.   Coarse-Particle Results 	291
     E-4.   VOC Results  	301
     E-5.   Meteorological Data	313
     E-6.   Linear Correlations Between Sites	315
     E-7.   PAH Results  	323
                                      111

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Table of Contents (cont'd)                                                    Page


F.   DIFFUSION/TRANSPORT MODELING	341
     F-l.   WV3 Eulerian Grid Dispersion Model	343
     F-2   Model Input  Source Emissions	345
     F-3.   Model Input - Meteorological Vertical Eddy Diffusivities	351
     F-4.   Model Input - Sampling Intervals  	355
     F-5.   Model Output  Simulations  	357
     F-6.   Development of the Mobilization Coefficient Model and Results for
           the Tacoma Tideflats	369

G.   INTEGRATION OF RESULTS  	379
     G-l.   Plots of Metal Particulate  Concentrations, Metal Deposition Rate,
           PAH Particulate  Concentrations, and PAH  Deposition  Rate for
           Sea-Land, Riverside, and Tyee Marina	381
     G-2.   One-Dimensional  "Contour" Plots of Measured TSP and Simulated
           PM10  	389
     G-3.   Contractor Reports and Publications Assessing  Performance of WV3
           Model   	401
     G-4.   Covariance Analysis	403
     G-5.   Tracer-Rose	409

H.   SUPPORTING DOCUMENTS  	415
                                       IV

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Appendix A. Literature Survey
A review was made of pertinent articles referred to us by members of the Technical Work
Team and EPA Region 10 staff. Additional material was acquired through libraries and by
reference from key researchers.

Each of the following subsections contains an overview of the important points from the
literature organized by topic.

MASS BALANCE

A number of studies performed in Puget Sound, the Great Lakes, Chesapeake Bay, and
elsewhere have attempted to define the sources and fates of various pollutants with respect to
a specific water body. Paulson et al. (1988b) describes the sources and sinks of lead (Pb),
copper (Cu), zinc (Zn), and manganese (Mn) in the main basin of Puget Sound. Sources for
the mass balance model (balance of incoming, outgoing, and resident chemicals) included
advectipn, riverine inputs, erosional inputs, municipal and industrial discharges, atmospheric
deposition, and diffusion from sediments. Mass balance estimates were based on measurements
taken along a transect down the central basin of Puget Sound. The paper suggests that the mass
balance approach may be most useful for addressing conditions in the main basin that are not
affected by local sources. Estimates of the metric tons per year (mt/yr) of metals input to the
Sound from atmospheric sources include: lead (Pb)~23 mt/yr; copper (Cu)~9 mt/yr; zinc (Zn)-
-7 mt/yr; and manganese (Mn)~2.7 mt/yr (uncertainties were estimated to be ±100 mt/yr).
Separate budgets for dissolved and particulate trace metals are described in a further analysis
(Paulson et al., 1988a). According to that study dissolved trace metals dominate conditions in
the water column while suspended particulate trace metals are rapidly lost due to settling.

Estimates of atmospheric deposition were also made in the Toxicant Pretreatment Planning
Study (Romberg et al., 1984) which was prepared for the Municipality of Metropolitan Seattle
(Metro). Fallout estimates were made using the following information: a lead/total suspended
particulate (Pb/tons per year) ratio measured at the University of Washington, the assumption
that this Pb/tons per year ratio is constant over the region, interpolated tons per year maps for
the region (provided by PSAPCA), and an assumed settling velocity of 1 cm/sec (Crecelius,
1981). The paper concludes that atmospheric deposition is a significant source of lead. The
relative importance of the atmospheric pathway for lead is likely to decrease with the increase
in use of unleaded gasoline. However, atmospheric deposition appears to be insignificant
compared to other sources for other metals. Similar calculations were made for polycyclic
aromatic hydrocarbons (PAHs) assuming the PAH/Pb ratio was stable. The paper concludes
that the atmospheric input of combustion derived PAHs is significant. An overview of this
work (Strayer and Pavlou, 1988) further concludes that PCBs found in Puget Sound originate
primarily from industrial discharges to the water. Additionally, it was concluded that detailed
monitoring and modeling appear to be required to obtain accurate estimates of nonpoint source
contributions (including widely dispersed air sources, advection, etc.) to Puget Sound.

A mass balance model was developed to explain measured concentrations of PAHs in Siskiwit
Lake on a wilderness island in northern Lake Superior (McVeety and Kites, 1988). Important
conclusions in this study include: dry deposition (the deposition of particulates during dry
weather conditions) was found to dominate the wet removal mechanism (removal of particles
from the atmosphere by both in-cloud and below-cloud processes) by an average ratio of 9:1;
aerosols (suspended particles) are transported long distances by the wind~the distance being a
function of particle size and wind speed; sedimentary PAH concentrations decrease dramatically
with distance from urban centers; a notable change in fluoranthene/pyrene ratios between
seasons indicate a summer dominance of automotive sources and a winter dominance of wood

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combustion sources; and aerosol washout (below-cloud scavenging of particles by water in the
liquid or solid form) dominates wet removal.

Estimates of atmospheric deposition of metals in Chesapeake Bay (Helz, 1976) support Puget
Sound estimates  in  concluding that  the  only  metal  with a high  percentage input from
atmospheric deposition is lead (Pb).  This conclusion is  further supported by work in the
Southern California Bight (Patterson and  Settle, 1974).  This latter work concludes that aerosol
deposition may account for much of the  lead introduced to oceans on  a world scale.

GREAT LAKES

Extensive research has been conducted on the importance of atmospheric deposition of pollutants
to the Great Lakes. Evidence pointing to the significance of an atmospheric pathway include
measurements of pollutants in remote lakes including some located on  islands within the Great
Lakes (Swackhamer et al., 1988).  In addition, high pollutant levels have been detected in both
wet and dry deposition samples at near-shore sampling sites.

Great  Lakes  studies  also provide the following  information  on  atmospheric  deposition
mechanisms and processes:

*   Wet deposition is the principal atmospheric removal process  for PCBs; 10 to 15 percent
    of the annual loading of pollutants to the lakes is contributed by one percent or  fewer of
    the precipitation events; most materials show much higher concentration in the  first few
    millimeters of rain; and the spatial variability of rain is quite high (40 to 50 percent of total
    precipitation is associated with thunderstorms) (Murphy, 1985).

*•   Difficulties were encountered while trying to calculate the vapor exchange (exchange of
    vapor between air and water surfaces)  and the mass transfer coefficient for these studies.
    The vapor phase equilibrium for  each compound  is a  function of the volatility and the
    solubility of that compound.  The mass  transfer coefficient is a function of wind speed,
    temperature, sea state, presence of the microlayer, and other  factors (Murphy, 1985).

*   Another method for estimating the  input from atmospheric deposition is to assume that
    during  stratification (the formation of layers  with respect to buoyancy) the upper layer of
    water is cut off from all direct inputs except  atmospheric.  Comparing profiles before and
    after stratification showed  uniform  concentrations of metals before stratification, and a
    higher concentration of metals above the thermocline (the area in the water  column where
    the temperature decreases  rapidly with depth) at the end of the  stratification season.
    Atmospheric deposition was assumed to be responsible for the metals concentrated near the
    surface (Murphy,  1985).

>•   Atmospheric deposition was estimated to be responsible for 60 to 80 percent of the PCBs
    found in the Great Lakes ecosystem  (Eisenreich et al., 1981).

>   In the PCB mass balance studies on Siskiwit Lake on Isle Royale in Lake Superior, wet
    deposition was estimated to be three times the dry deposition, deposition  with  rain was
    found to contribute more than deposition associated with snowfall, removal from the lake
    by volatization (evaporation) was found to be more important than sedimentation, and the
    average loss to the atmosphere by  volatilization was estimated to be 65 percent of the total
    loss (Swackhamer et al.,  1988).

*   An inventory of air emissions of 30  trace elements compared  to actual river inputs of Zn
    Cu,  and  nickel (Ni) indicated that the atmosphere  may be a major source of Zn!
    Atmospheric contributions of Cu and Ni may also be considerable. Fallout concentrations
    from sources at great distance depend  on wind direction and  speed, the altitude of the

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pollutants, the effectiveness of removal processes by "clear air deposition" (which is a
function of particle size distribution), and precipitation scavenging (collection by rain, snow,
sleet, etc.) which is a function of solubility (Winchester and Nifong, 1971).

>• Evidence suggests that precipitation scavenging of fine particles (<2 microns) and vapor
dominates atmospheric deposition at locations distant from major point sources or source
regions, while dry deposition of larger particles may be more important near the source.
In "clean" rural airsheds, low molecular weight PAHs were primarily in the gas phase,
while high molecular weight PAHs and dioxins were found primarily in the particle phase.
In contrast, a greater fraction of all of the pollutants were found in the particle phase in
"dirty" urban/industrial areas (Strachen and Eisenreich, 1988).

Atmospheric deposition studies in the Great Lakes have looked at three classes of chemicals:
organics, metals, and nutrients (Murphy 1985). Organic chemicals studied have included:
PAHs, PCBs, chlorinated dibenzodioxins and dibenzofurans, and pesticides (toxaphene, mirex,
DDT). Metals studied include mercury (Hg), cadmium (Cd), and Pb. Toxaphene is a pesticide
which has been found in the Great Lakes but is used only in the northern plains and in the
south. Therefore, long distance transport and atmospheric deposition has been the assumed
pathway for the introduction of this chemical. The pollutants chosen for the Great Lakes studies
were those found in the water in concentrations high enough to cause adverse and often
irreversible effects in fish and wildlife (Canadian Embassy Newsletter, 1988). The criteria for
the selection of monitored chemicals included:

* relevant toxicity
> quantities emitted
* likelihood of atmospheric pathway as important route of exposure, and
> feasibility of measurement in atmospheric samples

During the Great Lakes studies an extensive monitoring network was set up along with quality
assurance/quality control (QA/QC) protocols. Monitors in the Great Lakes network included:
high volume aerosol, wet and dry deposition, and meteorological/hydrplogical (precipitation,
snow, air and water surface temperature, humidity, wind speed and direction, water current
speed and direction, and wave heights). Researchers found that dry deposition collectors should
include water if estimates of dry deposition on the water surface are being made (Murphy,
1985). Water in the dry deposition collectors reduced resuspension of the deposited materials.
A design strategy for the Great Lakes monitoring network is outlined in Eisenreich's 1985
report on the Atmospheric Deposition Workshop on Organic Contaminant Deposition to the
Great Lakes Basin. The design strategy for this study combined monitoring and modeling.
Sixteen sites (both regional and urban) were chosen for the monitoring study, including two to
four "master" sites which are used for calibrations, comparisons, and research.

MICROLAYER

The sea surface microlayer forms the boundary between the atmosphere and the ocean. This
layer, approximately 50 microns in depth, has unique physical, chemical, and biological
properties (Hardy, 1982). Scientists studying the microlayer have found pollutant enrichments
at concentrations 100 to 10,000 times greater than in the water column which may be harmful
to organisms which come in contact with it (Hardy, 1984). A further consideration in the study
of microlayer contamination is the potential deposition on beaches from microlayer pollution
(the bathtub ring phenomenon).

Hardy et al. (1985b) estimated that the residence time of metals deposited from the atmosphere
in the microlayer ranged from 1.5 to 15 hours. The enrichment of the microlayer is a function
of wind speed and source strength (amount emitted by a source) and is enhanced by biological
activity. Pollutants are retained on the particles as organic complexes and can affect the neuston

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(biological organisms living in the surface layer of the water column) if biologically available.
Hardy assumes in this work that metal enrichment of the microlayer results primarily from dry
atmospheric deposition.

The enrichments of metals in the microlayer were found to be two to 15 times greater in Elliott
Bay (industrialized) than Sequim Bay (rural) (Hardy et al., 1985a). In the same study, metals
enrichments in the microlayer were found to be six to 65 times greater than in bulk water
samples for both bays. The concentrations of the metals measured in this study agreed well
with predictions of atmospheric deposition. The highest metal enrichments were found in slicks
(areas with high surface tension). Most metals are associated with particulates in the
microlayer. These particulates tend to concentrate in natural organic films and slicks which are
extremely patchy both spatially and temporally due to wind current and tidal patterns.
Therefore, it is necessary to sample the microlayer at closely spaced intervals both spatially and
temporally.

In an earlier paper (Hardy et al., 1984) it was pointed out that no studies had characterized
overall toxicities or bioavailabilities of typical atmospheric particulates to marine organisms.
However, it is important to note that Cu is particularly toxic to marine microalgae. PCBs,
other chlorinated hydrocarbons, plastic particles, petroleum derived hydrocarbons, and
combustion derived PAHs are all connected with negative biological effects (Hardy et al.,
1987b). Sources and pathways of toxic materials are described in a study of the concentration
and toxicity of sea-surface contaminants in Puget Sound (Hardy et al., 1986b). One source of
organic and metal pollutants to the surface layer are air bubbles which form in the water
column, transport particles to the water surface, and break at the water surface injecting
pollutants into the air where they may be redeposited on the sea surface. However, Hardy
estimates that up to half the total input of combustion PAHs and paniculate metals entering
coastal waters in some areas of the U.S. originate from atmospheric deposition. This estimate
was supported by high concentrations of PAHs measured in the urban microlayer while no
PAHs were found in the bulkwater samples (Hardy et al., 1986b). The highest concentrations
of PAHs measured in this study were found in Elliott and Commencement Bays. Combustion
and unburned fossil fuel PAHs were differentiated by using the
methylphenanthrene/phenanthrene (MP/P) ratio. Combustion PAHs have a MP/P ratio of less
than one which was typical of organic pollutants measured in Elliott Bay. Unburned fossil fuels
typically have MP/P ratios of two to six.

In a later study (Hardy et al., 1987c, d) PAHs were found in 57 percent of the microlayer
samples from Puget Sound. Lead, benzo(a)pyrene, and PCBs were reported in relatively high
concentrations in a 1988 paper (Hardy and Antrim, 1988a).

Studies in Chesapeake Bay (Hardy et al., 1987b and Gucinski et al., 1988) showed elevated
levels of metals and hydrocarbons in the microlayer, while bulkwater samples rarely had
detectible levels. These findings implicate atmospheric deposition and surface runoff sources.
Other potential sources of pollutants to the microlayer include hydrophobic or floatable materials
from wastewater discharge, hydrophobic materials released to the water column during dredging
operations (Hardy & Cowan, 1986), and PAHs from ocean incineration (Hardy and States
1986).

SEDIMENTS

Many toxicants released to Puget Sound collect in sediments. To quantify the effect of
atmospheric deposition on the Sound it is important to determine how much of a toxicant
remains in the Sound where organisms may be exposed to it. For example, an accumulation
of anthropogenic hydrocarbons in sediments is a potential threat to the health of the marine
environment (Bates et al., 1987). Several studies have used sediment data to better understand
the effect of toxicants on Puget Sound and other bodies of water.

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Studies by Bates et al. (1987) and Murphy et al. (1988) quantified PAHs on settling particles
and surficial bottom sediments. PAHs are a product of incomplete combustion of organic
materials. They reach Puget Sound via direct atmospheric deposition, river runoff, stormwater,
and municipal and industrial effluents. In the aquatic environment PAHs are readily adsorbed
onto particulate matter and subsequently deposited into the sediments. The larger the particulate
matter, the more quickly the particulates are incorporated into the sediment. Bates et al. (1987)
reported finding the highest concentrations of hydrocarbons in particulates in the surface waters
near Seattle, with decreasing particulate hydrocarbon concentrations with increasing depth and
distance from major urban areas. Sediment contamination did not necessarily reflect nearby
sources except in industrialized embayments. The major transport process in the central basin
of Puget Sound appears to be vertical flux through the water column to the sediments.
Resuspension and lateral transport in the bottom nepheloid layer also acted to redistribute PAHs
in the Sound. They concluded that fjord-like estuaries like Puget Sound act as traps for
hydrocarbons.

Murphy et al. (1988) found that more than 90 percent of hydrocarbons associated with
suspended particulates in the main basin of Puget Sound are deposited in estuarine sediments.
Sixty-three percent of the PAHs settle directly to sediments and the remainder are carried to the
main basin sediments via horizontal transport from other areas. Murphy et al. (1988) estimated
that approximately 18 percent of the PAH budget was attributable to atmospheric deposition.
Elevated hydrocarbon levels in estuarine waters and sediments can have an adverse effect on
marine life as cited in Murphy et al. (1988). Some examples of sediment concentrations of
PAHs from the sediment trap study by Bates et al. (1987) are 3,200 ng/g (ppb), 1,200 ng/g,
and 800 ng/g at 12 km, 37 km and 45 km (respectively) from the urban area.

Wakeham (1977b) used synchronous fluorescence to compare the aromatic hydrocarbon content
of Lake Washington sediments with samples of atmospheric dustfall, samples of sediments from
rivers which feed into Lake Washington, terrestrial plant material from local areas, mixed
plankton hauls from Lake Washington, and samples of urban stormwater. He found that the
primary source of petroleum hydrocarbons in surficial sediments is stormwater runoff.
Atmospheric dustfall is the primary source of aromatic hydrocarbons containing five or more
rings in the surface sediments of Lake Washington. The fluorescence spectra of surface
sediment hydrocarbons were similar to the spectra of hydrocarbons isolated from stormwater
runoff and atmospheric dustfall.

Broman et al. (1988) conducted a sediment trap study to examine the spatial and temporal
distribution of 18 PAH compounds and lead in the Stockholm archipelago. Using 16 sediment
traps they found a steep logarithmic decline in the concentration and fluxes of both PAHs and
lead with distance from urban areas. They determined that transportation and sedimentation of
seston (biological organisms living in the water column) is an important mechanism for
redistribution and incorporation of PAHs into the ecosystem. Their research also indicates that
nonpoint emissions in combination with direct runoff are probable carriers of PAHs.

In a mass balance study of the main basin of Puget Sound, Paulson et al. (1988) examined the
sources and sinks of Pb, Cu, Zn, and Mn. The sinks included advective transport and
sedimentation. They found that sediments of the waterways in Elliott and Commencement
Bays are highly contaminated with metals. They concluded that 70 percent of the Pb was
retained in underlying sediments, and that 40 percent of the Cu and Zn was deposited in the
sediments. Average sediment concentrations in Elliott Bay, Commencement Bay, and the main
basin were 90, 32, and 36 ppm for Pb, respectively; 88, 56, and 44 ppm for Cu, respectively;
and 165, 90, and 115 ppm for Zn, respectively.

Research in the Great Lakes has also included analyses of bottom sediments. McVeety et al.
(1988) measured PAHs in the sediments of remote Siskiwit Lake, a lake on an island in Lake

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Superior assumed to have only atmospheric sources of pollutants. They determined that 10 to
80 percent of the total output flux of PAH was due to surface volatilization depending on the
volatility of the PAH, and the remaining PAH was lost to sedimentation. Swackhamer et al.
(1986, 1988) determined that removal by volatilization was similar to sedimentation for PCBs
in Lake Michigan and four remote Wisconsin lakes. Volatilization losses were greater than
sedimentation for most similar chemicals in Siskiwit Lake. By comparing trace metal
atmospheric loading rates (derived from bulk deposition measurements) to estimated trace metal
sedimentation rates, Eisenreich (1980) determined that atmospheric deposition can account for
greater than 50 percent of trace metal accumulation in surficial sediments for Zn, Cu, Pb, Cd,
cobalt (Co), calcium (Ca), magnesium (Mg), and sodium (Na) in Lake Michigan.

STORMWATER RUNOFF

Stormwater runoff is a major mechanism for transporting toxicants that deposit on land surfaces
into Puget Sound. Urban runoff contains heavy metals, organic chemicals, nutrients, and other
pollutants. Most of the information cited on storm water runoff was obtained from studies
conducted as part of the Bellevue National Urban Runoff Program (Pitt and Bissonnette, 1984).
In this program the U.S. Geological Survey (USGS) intensively monitored two residential areas
and one urban arterial in Bellevue to determine urban runoff quality and quantity. Wet and dry
deposition were monitored and sampling was performed in small detention basins and creeks.

Urban stormwater runoff is a major source of phosphorus (P), Pb, and Zn, the most abundant
of which is Pb (Galvin et al., 1984). Lead is most commonly associated with airborne dust and
aerosols expelled from vehicle exhausts. Most metals are associated with suspended particulates
in urban runoff (Galvin, 1987). Two exceptions, Cu and Zn, are dissolved in the runoff.

Galvin et al. (1984) found that street dust and dirt on urban impervious surfaces are a major
contributor of toxicants to stormwater runoff. However, the constituents that settle as dustfall
are not necessarily the same as those of locally measured atmospheric suspended particles.
Concentrations of metals and PAHs associated with airborne particles are generally in the part
per million range. Much of this represents contaminants adsorbed onto sub-micron particles,
and these particles are not as likely to contribute directly to local street dust and runoff loads.
Fine particles account for only a small portion of the total loading of solids on street surfaces.
Atmospheric suspended PAHs are generally the larger, more complex compounds (three- to
five-ring) associated with fossil fuel combustion. PAHs in street dust tend to be smaller, two-
to three-ring compounds which are more likely to originate from used lubricating oil. Some
contribution to street dust PAHs may come from atmospheric deposition, but the majority
probably comes directly from dripping and exhaust fallout onto road surfaces from motor
vehicles. Pitt and Bissonnette (1984) also suggest that airborne PAHs are combustion products
while the street dirt PAHs are from petroleum product spills. Galvin et al. (1984) found that
although information does exist which supports a model of regional air pollutant fallout as a
contributor of at least some substances to surface contamination, there were no correlations
between metals and organics sampled in atmospheric suspended particles with those sampled in
street dust.

Hubbard (1988) discusses many of the sources of pollution in stormwater runoff. Sources
which contribute to stormwater pollution include atmospheric deposition, street dust, industrial
activities, highway runoff, commercial areas, residential areas, construction activities, and other
land uses such as agricultural uses, landfills, failing septic systems, and airports.

Mass loadings in stormwater runoff are strongly influenced by the amount of precipitation and
runoff (EPA, 1983). Prych et al. (1986) also found a negative correlation between precipitation
quantity and the concentration of chemical constituents. They determined that precipitation is
often a major source of pollution (particularly nitrate, nitrite, ammonia, and nitrogen) to urban

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runoff. For example, about one-third of the total nitrogen in stormwater runoff originates from
nitrogen in rainfall.

The Bellevue Urban Runoff Program has helped establish a better understanding of contaminants
present in stormwater runoff, but there has been little work on the percentage of toxicants in
the runoff that may be attributable to atmospheric deposition. Prych et al. (1986) estimated that
anywhere from one to 43 percent of the total recoverable Po in runoff loads was due to
constituents present in precipitation.

PAHS AND PCBS

PAHs are widely distributed in soils and sediments throughput the world. They are
environmentally significant because particular compounds are carcinogenic (Prahl et al., 1984).
PAHs are a product of incomplete combustion of organic materials, especially fossil fuels and
fossil fuel products.

Prahl et al. (1984) used atmospheric and sediment information to evaluate the relative roles of
atmospheric deposition and the Columbia River as sources of PAHs to Washington coastal
sediments. The composition of the PAH mixture contained in the atmospheric paniculate matter
collected at Quillayute, Sequim, and Seattle indicated that fuel materials were the dominant
source of PAHs in all cases. The authors noted a subtle seasonal trend in the concentrations
of PAHs measured in the atmospheric particulate matter, with maximum concentrations during
winter and minimum concentrations during summer. One possible explanation for this trend
is the elevated use of heating fuel in winter. Gasoline burning was another source of PAHs
mentioned in this article.

Average individual PAH concentrations in atmospheric particulate matter sampled in Seattle
were 2.5 to six times greater than those measured at either Sequim or Quillayute. This can be
explained by the major combustion PAH contributions from various anthropogenic processes
in Seattle; the PAH burden of the air in western Washington is strongly influenced by local
anthropogenic sources. Using PAH aerosol measurements and a deposition velocity assumed
to be 0.4 cm/s, Prahl et al. (1984) determined that less than 10 percent of the measured
accumulation rates for any individual combustion PAH in coastal sediments can be derived from
direct atmospheric deposition of particulate matter. In contrast, riverine suspended particulate
material from the Columbia River could supply greater than 30 percent of all combustion PAH
in coastal sediment.

Most of the information obtained on the atmospheric deposition of PCBs was derived from
studies of the Great Lakes. Interest in PCBs in the Great Lakes region began when high
concentrations of PCBs were found in the larger fish in Lake Michigan. PCB usage has been
curtailed since the early 1970s yet the compound and its derivatives continue to be found in the
lakes. Research indicates that PCB transport may have an important atmospheric component,
but quantification of the PCB flux across the air/water interface is difficult (Doskey et al.,
1981). Accurate measurements of PCBs in the atmosphere have been hampered by technical
and analytical problems. At the time of their research, Doskey et al. (1981) found there was
no uniformly accepted method for measuring airborne PCBs. They used a model to determine
the flux of PCBs across the air/water interface in Lake Michigan. Their calculations indicate
that the atmospheric pathway plays a major role in the input of PCBs to Lake Michigan in
comparison to other pathways.

Swackhamer et al. (1986) used sediment data from Lake Michigan and four remote Wisconsin
lakes to determine the atmospheric deposition of PCBs to the lakes. The four Wisconsin lakes
are isolated from point sources and so that atmospheric deposition is assumed to be the only
source of PCBs. It was also assumed that the remote lakes and Lake Michigan would receive
similar atmospheric loadings. The flux of PCBs to Lake Michigan was four times greater than

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the average loading to remote lakes. Swackhamer et al. determined that total atmospheric and
net non-atmospheric contributions to Lake Michigan were of similar magnitude. The
atmosphere above Lake Michigan acts as a sink (through volatilization) for PCBs, as well as
a source. In the remote lakes volatilization back to the atmosphere accounts for more than half
the losses from the water column, with the rest of the PCBs being lost to the sediments.

Studies by Eisenreich et al. (1979), Murphy et al. (1977), and Swackhamer et al. (1978) also
indicate that atmospheric deposition may be a major source of PCBs to the Great Lakes.

MODELING

Models are available in an array of sizes and functions. Comprehensive models are available
which attempt to include all the sources and sinks of pollutants affecting a waterbody. These
models necessarily rely on literature estimates for such difficult to quantify factors as the
settling velocity of air particles or the vapor transfer at the water surface. Other models attempt
to focus on one or another aspect of the problem in great detail. There is presently no model
which correctly describes all the processes involved in estuarine pollution. However, the
following models were considered for use in this study.

WYNDvalley (Harrison, 1988) is a Eulerian grid air quality dispersion model with versatile
boundaries, sources, and winds. It has been used to estimate particulate concentrations in
complex terrain for low wind speeds.

STORM (Harrison, 1986) has been used to estimate the effects of varying emission rates on the
concentrations of nitrogen and sulfur oxides in the air and rain, and their fluxes to the surface
through both wet and dry processes. This model can be adapted to various spatial scales and
source matrices, and therefore could be used to predict or verify aerosol concentrations and wet
and dry deposition over a watershed.

A sediment box model (Boehm et al., 1985) was designed as a conceptual framework relating
the residence time of contaminants in sediments to the recovery rates of a variety of benthic
community ecosystems. The main result of the study was to identify critical data gaps and to
guide future research and monitoring studies.

Slinn et al. (1978) address the known and unknown aspects of wet and dry fluxes across the air-
sea interface. This review paper emphasizes future research required to improve predictions
of atmospheric removal processes and residence times.

Multibox resistance models were used to describe continuum mass transfer processes (Sehmel
and Sutler, 1974). Improved versions can be used to predict deposition velocity as a function
of particle diameter, friction velocity, aerodynamic surface roughness, and particle density.

A computer model has been developed by personnel from the California Air Resources Board
and the California Institute of Technology based on Sehmel's work. The model predicts
gravitational settling velocities and deposition velocities for various particles given stability
class, wind speed, ambient temperature, surface roughness height, and the density and diameter
of the particles.

Hunsaker et al. (1987) describe a simplified model used to classify the pollutant status of
estuaries. The model uses two key components: loading rates, and fate and effects of
pollutants in the environment.

-------
MISCELLANEOUS

Long (1982) analyzed metals, PAHs, and synthetic organics in the sediments of Puget Sound.
He found the highest concentrations in Commencement Bay and Elliott Bay, but contaminants
were reported in all parts of Puget Sound that were sampled.

Barrick et al. (1982) quantified the flux of aliphatic and polycyclic aromatic hydrocarbons to
central Puget Sound from Seattle primary sewage effluent (West Point). They found that the
average discharge of aliphatic hydrocarbons was 475 metric tons/year, and the average
discharge of three- to seven-ring PAHs was 1 metric ton/year. PAHs with more than four rings
are principally derived from stormwater contributions.

Two articles discuss acid rain. The Department of Ecology's acid deposition program sampled
precipitation deposition at several sites throughout Washington. They measured sulfate, nitrate,
pH, and several cations (positively charged ions). The average levels of sulfate, nitrate, and
pH in the precipitation in Washington are not within the range believed to cause environmental
deterioration or adverse health effects.

Fisher et al. (1988) studied nitrogen deposition in Chesapeake Bay. They found that one
quarter of all the nitrogen contributed by human activity to Chesapeake Bay originates in acid
rain and associated dry deposition falling directly on the bay or the watershed. The authors
found that acid rain is surpassed only by fertilizer runoff as a source of nitrogen to Chesapeake
Bay.

Galloway et al. (1982) reviewed the present knowledge of the atmospheric deposition
characteristics of 19 toxic metals. Most of the data were for bulk deposition, although in some
cases both dry and wet deposition were measured. They concluded that dry deposition may be
substantial in comparison to wet deposition for many situations.

Crecelius (1981) used total Beryllium-7 deposition velocities and elemental air particulate data
to predict elemental deposition rates at specific marine sites. Beryllium-7 is usually attached
to submicron air particles, and should have the same deposition velocity as anthropogenic
pollutants that attach to submicron particles in the atmosphere.

Buat-Menard et al. (1979) measured 17 trace metals in the marine atmosphere and in the deep
water of the Tropical North Atlantic. They found that the primary flux of aluminosilicates is
due to atmospheric sources. The atmosphere is also the dominant source of particulate selenium
(Se) and Pb in seawater.

Cambray et al. (1979) estimated the atmospheric deposition of particulate trace elements to the
North Sea by determining the mean concentration of these elements in rainwater. They
determined that atmospheric deposition was a significant source of trace elements to the North
Sea.

Hawthorne et al. (1988) showed that methoxylated phenols are unique to woodsmoke in the
urban atmosphere and are therefore recommended as good tracers for atmospheric wood smoke
pollution.

Crecelius (1980) studied the solubility of coal fly ash and marine aerosols in seawater and
found that the solubility of the chemicals is different when they are associated with different
matrices. The solubility of the chemical depends on how tightly bound the chemical is within
the matrix of the complex compounds.

-------
PUGET SOUND SUMMARY

The percentages  of Pb, Cu,  Zn, and  Mn present in the Sound which  originated from
atmospheric sources have been estimated in mass balance studies  using Puget Sound data.
While the atmospheric source contribution  was significantly higher for lead than the other
metals considered, major sources of airborne lead have  decreased  markedly in recent years
(largely due to the increased use of unleaded gasoline).

Microlayer enrichments  of metals, PAHs, and PCBs have been measured in a few places in
Puget Sound. Metals and PAH enrichments were significantly greater in urban than rural bays.
Combustion and fossil fuel PAHs can be differentiated using PAH tracer ratios.

PAHs have been quantified on settling particles and  surficial bottom sediments.   The highest
sediment concentrations  were found near urban areas; sediment concentrations decrease with
increasing depth and distance from urbanized bays.  The highest sediment concentrations of
metals, PAHs, and synthetic organics were found in Commencement and Elliott Bays.

Estimates  using available aerosol  data lead to  the conclusion that  the atmosphere can be a
significant pathway to the Sound for some metals and PAHs.  Although PCBs have also been
reported in high concentrations in the sediments, experts believe these  substances are contributed
by municipal and  industrial outfalls rather than by air emission sources.
                                          10

-------
Appendix B.  Meteorological Data
      B-l.  Hourly Meteorological Data	  13
      B-2.  24-Hourly Meteorological Data	93
      B-3.  Air Stagnation Episodes  	99
      B-4.  Data for Air Stagnation Analysis	107
                                     11

-------
Appendix B-l. Hourly Meteorological Data
                                        13

-------
YEAR DAY HR   WS  WD
             M/S PEG
SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
 M/S   PEG  PEG    °C    °C   W/M^2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
191
191
191
191
191
191
191
191
191
191
191
191
191
191
191
191
191
191
191
191
191
191
191
191
192
192
192
192
192
192
192
192
192
192
192
192
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
1.5
1.6
1.3
1.2
1.7
2.1
2.4
2.9
3.3
3.2
2.9
3.2
2.5
2.3
2.7
3.0
3.1
4.5
4.4
3.3
3.0
3.3
2.5
2.7
2.4
2.2
2.1
2.0
2.4
2.1
2.2
2.3
2.6
2.4
1.8
1.5
1.2
1.1
1.2
1.6
1.9
1.9
1.1
1.0
1.0
1.3
1.3
1.2
.8
.6
1.1
1.1
.8
2.1
2.6
3.5
4.2
4.2
315.
306.
309.
315.
289.
274.
280.
281.
283.
283.
288.
295.
312.
300.
208.
174.
197.
250.
254.
248.
238.
240.
202.
176.
181.
197.
198.
188.
201.
211.
179.
205.
238.
236.
203.
237.
143.
141.
109.
156.
153.
137.
114.
135.
230.
306.
204.
330.
98.
121.
334.
180.
185.
277 .
277.
279.
282.
284.
.303
.246
.284
.242
.212
.265
.328
.442
.608
.464
.683
.611
.586
.591
.666
.655
.604
.747
.834
.786
.568
.625
.474
.480
.513
.466
.438
.433
.531
.499
.453
.542
.617
.535
.506
.577
.472
.408
.554
.492
.454
.390
.286
.218
.203
.214
.374
.341
.336
.297
.321
.289
.217
.271
.319
.406
.508
.622
10.5
6.7
9.1
10.5
7.2
8.2
10.7
9.1
11.2
10.1
16.6
16.2
18.5
18.3
18.8
12.2
11.9
8.9
9.9
12.5
10.3
9.3
11.0
9.2
11.0
10.5
10.3
14.5
12.7
14.2
13.0
13.1
12.8
12.9
19.2
25.3
27.5
29.3
28.0
21.0
12.6
10.3
13.8
11.6
15.5
12.2
19.1
18.8
34.2
28.9
15.5
24.8
18.3
7.7
7.2
6.8
7.2
8.1
11.2
8.6
15.3
17.5
13.1
10.8
15.9
11.0
12.4
12.2
24.3
23.9
33.1
32.6
71.1
17.3
29.4
10.3
11.2
14.3
13.4
11.3
30.1
10.6
12.4
11.2
14.4
31.6
26.2
31.0
15.9
27.9
18.9
17.1
31.5
29.9
66.6
45.4
49.0
33.6
15.9
16.9
26.4
25.1
52.4
23.8
29.2
21.8
55.5
56.9
20.4
69.0
51.4
9.3
8.1
7.4
8.5
8.9
13.9
13.5
13.5
13.6
14.0
15.3
16.5
17.2
18.0
18.5
20.1
21.3
22.1
21.7
20.8
19.9
19.7
18.7
17.2
16.1
15.6
15.5
15.2
14.9
14.8
14.7
14.6
14.7
14.8
15.1
15.3
15.6
16.1
16.4
17.1
18.2
19.2
19.8
20.8
20.3
20.0
19.1
17.5
17.5
16.2
15.2
14.0
13.7
12.6
12.2
12.6
12.7
13.7
15.1
16.5
18.4
20.0
21.1
-.07
-.08
-.13
-.06
-.14
-.41
-.60
-.80
-.94
-.97
-1.29
-1.63
-1.66
-1.13
-.54
-.34
-.39
-.28
-.20
-.24
-.24
-.25
-.20
-.15
-.16
-.18
-.16
-.13
-.21
-.25
-.30
-.33
-.46
-.47
-.54
-.63
-.96
-.93
-1.37
-.68
-.35
.04
.49
.38
.54
.23
.50
.25
1.08
1.01
.39
.27
.12
-.33
-.60
-.90
-1.17
-1.27
0.
0.
6.
104.
244.
451.
474.
583.
638.
646.
921.
889.
569.
439.
230.
95.
94.
27.
0.
0.
0.
0.
0.
0.
0.
0.
1.
7.
33.
68.
100.
96.
163.
160.
313.
305.
298.
246.
346.
195.
119.
15.
0.
0.
0.
0.
0.
0.
0.
0.
7.
97.
246.
447.
622.
768.
862.
941.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                       16

-------
YEAR DAY HR   WS  WD
             M/S  PEG
SDWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
                    °C    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
192
192
192
192
192
192
192
192
192
192
192
192
193
193
193
193
193
193
193
193
193
193
193
193
193
193
193
193
193
193
193
193
193
193
193
193
194
194
194
194
194
194
194
194
194
194
194
194
194
194
194
194
194
194
194
194
194
194
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
3.9
2.9
1.9
2.6
2.1
2.1
2.2
2.3
1.9
1.0
1.8
1.1
1.2
1.3
1.3
1.1
1.0
.7
1.8
3.3
2.5
1.8
3.7
3.0
3.0
2.3
2.2
1.8
2.8
4.1
4.0
4.1
3.8
3.5
1.6
2.3
2.2
2.5
2.1
1.6
1.9
2.1
1.2
1.6
2.2
1.8
2.7
1.9
2.7
2.0
2.4
2.2
2.3
2.0
1.9
1.7
1.6
1.5
288.
308.
244.
280.
307.
323.
314.
297.
306.
187.
266.
148.
312.
149.
282.
211.
146.
197.
277.
290.
297.
240.
283.
265.
228.
150.
288.
264.
288.
284.
260.
244.
254.
263.
236.
181.
198.
229.
235.
197.
222.
258.
183.
272.
335.
306.
293.
278.
277.
244.
295.
295.
282.
321.
286.
309.
311.
244.
.613
.832
.695
.538
.618
.622
.510
.540
.624
.482
.545
.443
.367
.443
.409
.362
.288
.287
.319
.436
.510
.782
.534
.636
.868
.798
.611
.508
.601
.718
.706
.826
.955
.689
.374
.489
.433
.436
.362
.387
.463
.511
.416
.429
.455
.443
.487
.574
.708
.652
.767
.584
.594
.480
.485
.383
.338
.374
11.7
22.4
34.9
18.3
27.2
20.7
16.6
16.4
30.2
56.8
19.8
24.6
20.0
21.1
27.4
33.0
25.3
30.9
10.9
7.4
17.1
36.4
8.2
15.0
20.0
28.1
21.7
26.1
11.6
9.4
9.6
12.2
14.4
9.5
15.3
10.8
9.3
8.7
8.1
13.4
14.8
14.1
28.5
25.6
13.6
19.6
17.1
32.8
15.9
30.4
22.6
19.2
15.9
20.2
15.8
16.9
12.1
16.4
13.7
29.2
52.0
24.9
32.5
26.4
27.6
27.6
37.9
93.5
38.1
34.6
24.8
29.1
55.3
91.8
56.3
87.0
15.1
11.0
27.5
46.0
9.4
33.1
29.6
35.8
28.1
41.7
15.3
18.0
13.5
13.1
16.2
11.4
41.6
13.7
19.1
13.2
14.8
22.8
20.1
20.7
45.8
85.0
19.9
39.0
30.6
43.1
19.7
37.0
29.5
28.2
18.2
32.6
21.3
23.5
22.1
30.2
22.3
24.1
25.3
25.2
26.3
26.5
25.1
22.6
20.4
19.4
18.2
16.8
16.4
15.7
15.7
15.3
14.1
15.0
16.4
17.1
19.5
22.1
22.1
24.4
27.7
29.1
27.6
28.8
28.7
26.9
25.0
22.3
20.1
18.9
18.1
17.3
16.5
16.1
15.5
15.3
15.3
15.4
15.6
15.5
15.5
16.1
16.6
17.3
18.6
20.4
21.6
22.5
22.8
24.5
24.5
21.0
19.3
18.1
-1.31
-1.68
-2.18
-1.41
-1.73
-1.88
-1.14
-.68
0.00
.07
.13
.63
.28
.60
.26
.45
.92
.56
-.31
-.55
-.59
-1.36
-1.20
-1.78
-3.53
-3.73
-1.45
-1.17
-.99
-.12
-.56
-.31
-.13
-.13
.06
-.05
-.07
-.10
-.16
-.11
-.16
-.27
-.28
-.47
-.56
-.69
-.81
-.75
-1.03
-1.47
-1.63
-1.42
-1.23
-2.32
-2.20
-.39
.15
.28
957.
916.
736.
648.
540.
347.
183.
45.
1.
0.
0.
0.
0.
0.
0.
0.
8.
125.
283.
442.
607.
755.
863.
929.
939.
906.
815.
677.
516.
272.
129.
36.
0.
0.
0.
0.
0.
0.
0.
0.
2.
45.
64.
70.
75.
290.
373.
356.
651.
879.
796.
671.
513.
333.
167.
35.
1.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                       17

-------
YEAR DAY HR   WS  WD
             M/S PEG
SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
 M/S   PEG  PEG    °C    °C   W/M"2	IN.
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
194
194
195
195
195
195
195
195
195
195
195
195
195
195
195
195
195
195
195
195
195
195
195
195
195
195
196
196
196
196
196
196
196
196
196
196
196
196
196
196
196
196
196
196
196
196
196
196
196
196
197
197
197
197
197
197
197
197
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
2.0
1.5
2.0
1.8
1.6
1.3
1.4
2.0
1.9
2.0
2.1
1.5
1.4
1.9
1.9
1.4
1.3
1.2
1.2
2.3
3.6
2.9
3.1
3.3
3.9
3.3
2.4
2.5
2.6
2.2
2.2
2.0
2.8
3.3
3.5
3.0
3.0
3.9
4.2
2.9
4.2
5.0
4.1
4.4
4.0
3.9
3.8
2.8
1.5
1.6
1.2
1.1
1.2
.8
.7
1.8
1.7
1.3
305.
310.
311.
301.
316.
304.
310.
291.
300.
284.
291.
283.
310.
280.
294.
252.
228.
122.
164.
202.
270.
272.
247.
241.
256.
239.
181.
182.
165.
133.
159.
172.
160.
173.
214.
214.
232.
229.
216.
225.
248.
243.
237.
234.
243.
249.
257.
244.
228.
210.
222.
240.
275.
196.
108.
138.
154.
137.
.377
.282
.431
.300
.312
.254
.266
.320
.332
.271
.274
.330
.555
.556
.456
.352
.302
.435
.457
.612
.640
.778
.590
.882
.716
.654
.537
.682
.566
.411
.438
.446
.566
.720
.877
.660
.729
.822
.865
.827
.844
.887
.772
.834
.665
.652
.588
.611
.335
.344
.272
.154
.180
.179
.240
.287
.282
.300
9.7
11.0
10.5
7.8
11.4
8.4
11.5
8.9
12.1
7.2
8.0
10.9
31.7
20.5
17.9
15.8
16.8
26.9
29.0
17.0
10.3
14.7
14.2
13.3
11.0
10.3
15.5
13.1
13.0
12.1
12.2
12.1
11.2
12.9
15.7
15.7
15.9
16.6
12.4
18.7
10.7
10.3
12.0
10.8
8.6
8.7
9.4
10.4
14.5
15.8
13.3
8.7
9.5
13.9
23.0
8.6
8.6
15.8
16.2
17.3
13.7
9.5
16.3
9.6
20.3
13.2
19.8
7.8
13.8
19.4
39.9
23.1
32.9
21.8
21. 1
64.1
97.9
69.5
14.7
19.2
21.4
18.2
11.9
15.9
18.5
16.2
22.1
19.3
26.4
18.3
19.7
27.1
20.3
20.6
18.1
21.4
17.3
25.4
13.3
13.5
13.2
13.1
12.1
9.8
10.4
15.3
20.7
23.5
19.9
21.9
37.5
28.0
54.4
15.7
9.9
19.7
17.8
17.1
16.3
15.7
15.5
15.4
15.2
15.3
15.8
16.1
16.6
17.6
19.1
19.7
20.6
21.5
22.5
24.3
24.2
22.9
21.5
20.5
19.1
17.8
16.6
16.0
15.5
14.7
14.1
13.8
14.3
14.6
15.6
16.7
17.4
17.9
18.8
19.5
19.3
19.9
20.1
19.8
19.5
19.2
18.8
18.3
17.8
17.3
16.9
16.6
16.5
16.1
15.1
14.3
14.1
14.0
14.4
15.2
-.09
.05
.09
-.03
-.07
-.15
-.18
-.28
-.40
-.45
-.48
-.58
-.87
-.61
-.97
-.89
-.88
-2.09
-1.36
-.55
-.29
-.20
-.22
-.24
-.19
-.12
-.08
-.08
-.01
.13
-.05
-.04
-.27
-.41
-.52
-.57
-.75
-.77
-.67
-.75
-.76
-.65
-.60
-.43
-.24
-.17
-.15
-.16
-.06
-.11
-.10
.04
.09
.03
-.05
-.03
-.14
-.27
0.
0.
0.
0.
0.
0.
6.
68.
128.
154.
160.
276.
348.
464.
442.
501.
468.
290.
317.
123.
40.
8.
0.
0.
0.
0.
0.
0.
0.
0.
1.
30.
264.
315.
337.
318.
388.
437.
353.
369.
361.
320.
226.
113.
43.
7.
0.
0.
0.
0.
0.
0.
0.
0.
1.
20.
59.
118.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.02
.04
.05
.02
.00
.00
                                       18

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
199
199
199
199
199
199
200
200
200
200
200
200
200
200
200
200
200
200
200
200
200
200
200
200
200
200
200
200
200
200
201
201
201
201
201
201
201
201
201
201
201
201
201
201
201
201
201
201
201
201
201
201
201
201
202
202
202
202
HR
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
WS
M/S
3.6
2.9
2.3
1.1
.9
1.5
1.9
2.2
2.1
1.6
2.2
1.5
2.1
1.5
1.4
2.1
2.4
3.5
4.1
4.1
3.9
3.6
2.8
2.2
3.9
3.4
2.9
2.4
1.7
1.6
.9
.8
.7
1.4
1.5
1.7
2.0
1.4
1.4
.9
1.8
3.1
3.0
3.7
4.5
4.5
4.7
3.9
4.0
4.0
2.1
1.2
1.8
1.1
1.9
2.4
2.1
1.8
WD
DEC
296.
283.
323.
320.
193.
267.
245.
250.
250.
243.
249.
249.
250.
290.
317.
300.
280.
306.
318.
334.
341.
309.
299.
314.
93.
314.
312.
324.
321.
322.
307.
298.
251.
304.
292.
262.
227.
268.
284.
175.
274.
269.
227.
234.
244.
244.
250.
257.
251.
244.
269.
241.
230.
163.
173.
158.
160.
168.
SOWS
M/S
.666
.606
.465
.308
.252
.351
.386
.436
.430
.410
.421
.370
.518
.463
.379
.639
.756
.873
.995
.872
.843
.802
.706
.652
.793
.933
.597
.595
.326
.357
.214
.279
.207
.202
.280
.406
.433
.447
.484
.462
.633
.699
.703
.847
.831
.951
.984
.847
.905
.885
.703
.635
.859
.479
.520
.391
.345
.414
SDWD
DEC
9.3
11.9
11.6
12.2
24.7
10.6
10.3
10.7
11.1
12.0
10.4
12.5
11.7
16.4
21.6
23.3
19.3
15.4
16.9
15.0
14.0
14.9
17.1
22.5
10.1
15.2
13.8
14.8
11.5
11.0
15.5
23.1
21.5
7.9
9.2
11.4
13.4
27.8
24.5
39.1
20.3
18.1
13.5
16.1
9.8
13.0
10.7
12.5
11.6
11.2
22.1
46.5
31.7
37.3
18.5
7.8
9.4
11.6
SDEPA
DEC
10.1
21.0
12.6
25.4
78.5
15.5
13.6
12.7
13.0
17.1
14.1
13.3
12.9
21.0
31.9
28.4
26.9
20.0
19.7
18.2
15.1
24.5
21.5
30.3
14.9
18.6
19.1
17.2
16.7
15.8
22.9
29.2
44.9
10.6
11.3
29.6
16.4
37.3
34.3
90.7
27.4
39.3
15.9
18.4
11.7
16.2
12.2
13.9
12.8
12.7
29.1
62.9
35.6
55.4
25.5
9.4
11.4
12.6
TEMP
°C
23.4
21.1
19.8
19.7
19.4
19.0
19.1
18.8
18.2
17.8
17.5
17.2
17.6
18.0
19.0
20.3
21.1
22.0
23.0
24.5
25.1
24.4
24.7
25.5
23.8
20.3
18.2
17.6
16.5
15.9
15.0
14.8
14.9
14.7
14.3
14.4
14.8
15.3
16.8
18.0
19.0
19.1
19.8
20.6
19.9
20.7
20.5
19.6
19.1
18.4
17.5
16.6
16.3
15.6
15.2
14.3
13.4
13.3
DTDZ
°C
-.45
-.49
-.30
-.13
-.03
-.13
-.13
-.10
-.12
.01
-.09
-.07
-.27
-.32
-.67
-.76
-.99
-1.18
-1.46
-2.53
-2.72
-1.32
-1.07
-1.51
-2.32
-.74
-.02
.09
.10
.13
.47
.41
.31
.14
.11
-.07
-.35
-.44
-1.27
-.88
-.71
-.55
-.64
-.72
-.60
-.86
-.66
-.35
-.25
-.19
-.06
.04
-.04
.24
.27
.27
.16
-.05
SOLRAD
W/M^2
159.
15.
0.
0.
0.
0.
0.
0.
0.
0.
5.
56.
158.
215.
346.
797.
881.
946.
980.
937.
828.
693.
533.
351.
150.
38.
1.
0.
0.
0.
0.
0.
0.
0.
2.
43.
127.
209.
276.
443.
487.
209.
319.
354.
250.
530.
283.
110.
59.
22.
0.
0.
0.
0.
0.
0.
0.
0.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
20

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP   DTDZ  SOLRAD PCPN
              M/S DEG    M/S    DEG  DEG    °C    Or>   ™/M*.O  Tia
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
202
202
202
202
202
202
202
202
202
202
202
202
202
202
202
202
202
202
202
202
203
203
203
203
203
203
203
203
203
203
203
203
203
203
203
203
203
203
203
203
203
203
203
203
204
204
204
204
204
204
204
204
204
204
204
204
204
204
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
1.6
1.3
1.8
2.0
1.7
1.7
1.9
1.7
1.8
2.6
3.7
2.9
3.8
3.7
3.9
4.6
4.0
3.5
1.6
1.2
.9
.7
.5
.5
.9
.9
1.7
2.8
3.3
3.8
3.3
4.1
4.4
5.1
5.1
4.7
4.6
4.2
3.6
2.7
1.2
.9
1.6
1.2
2.5
1.1
1.2
1.5
1.2
1.4
1.2
1.0
2.3
2.0
1.9
3.7
4.0
4.0
190.
202.
206.
244.
219.
298.
293.
268.
267.
284.
293.
279.
238.
69.
124.
8.
14.
15.
68.
115.
127.
151.
227.
257.
187.
132.
61.
11.
151.
100.
145.
334.
337.
353.
350.
344.
288.
344.
348.
346.
281.
146.
245.
302.
313.
229.
120.
137.
140.
128.
116.
257.
302.
319.
289.
326.
326.
303.
.416
.359
.442
.522
.471
.554
.583
.569
.487
.702
.930
.747
.936
.867
.843
.931
.954
1.016
.669
.437
.358
.316
.203
.232
.213
.233
.822
.885
.946
1.142
.912
1.040
1.177
1.294
1.202
1.061
1.127
.982
.838
.733
.404
.299
.387
.319
.436
.261
.122
.138
.134
.116
.228
.339
.522
.564
.657
.843
.877
.796
14.2
17.5
14.6
18.6
27.7
25.3
22.2
23.4
19.7
18.1
16.6
20.1
16.8
16.0
13.6
11.4
13.5
16.6
27.0
33.5
27.9
37.4
28.1
35.0
15.1
23.0
33.9
16.7
17.4
17.4
20.5
16.1
16.4
14.4
15.1
13.9
13.9
13.5
13.4
14.9
28.8
37.4
10.1
13.2
8.2
20.7
8.3
4.9
4.7
3.3
11.5
31.0
15.4
23.3
24.5
14.1
13.5
13.5
15.2
27.1
23.7
24.5
33.5
36.3
35.6
25.9
26.2
23.5
17.9
32.6
20.0
17.5
15.5
11.6
13.9
17.0
28.8
60.2
54.7
86.2
91.0
47.7
74.2
29.5
52.3
17.6
19.2
21.1
28.2
18.0
18.1
15.0
16.3
14.4
16.1
15.3
13.6
15.5
43.8
77.2
20.9
23.0
10.1
35.9
14.7
11.7
8.9
6.6
22.3
49.1
17.5
40.2
28.4
17.4
21.9
16.2
13.4
13.8
14.2
14.5
15.0
16.6
17.7
19.2
21.0
22.1
23.0
23.5
25.0
24.4
22.1
19.5
17.5
16.3
15.6
15.0
14.1
13.6
13.1
12.2
11.5
12.0
14.9
16.5
17.9
19.8
20.8
21.4
22.8
24.5
25.2
25.5
25.4
24.8
23.9
21.7
19.0
17.1
16.4
14.9
14.7
13.1
10.6
10.5
10.1
10.8
13.2
15.1
16.5
18.4
20.0
21.4
22.9
23.7
-.12
-.19
-.20
-.42
-.48
-1.01
-1.07
-1.08
-1.45
-1.34
-1.52
-1.82
-3.37
-3.22
-1.96
-.56
.08
.14
.37
.62
.99
.70
.93
1.23
1.67
1.09
-.16
-.96
-1.22
-2.23
-2.23
-1.71
-2.27
-3.14
-3.17
-3.03
-2.72
-2.28
-1.85
-.63
.14
1.03
.62
.89
.20
.86
2.36
1.68
1.57
1.03
-.22
-.13
-.51
-1.16
-1.03
-1.63
-1.85
-1.34
*" *••» — &
1.
35.
147.
165.
321.
593.
876.
958.
974.
938.
803.
667.
521.
328.
154.
28.
0.
0.
0.
0.
0.
0.
0.
0.
4.
94.
262.
446.
619.
772.
882.
941.
955.
923.
832.
696.
535.
346.
172.
33.
0.
0.
0.
0.
0.
0.
0.
0.
3.
87.
233.
428.
604.
757.
870.
932.
946.
910.
	 -*--*-3 	
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                        21

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
207
207
207
207
207
207
207
207
207
207
207
207
207
207
207
207
207
207
207
207
207
207
207
207
208
208
208
208
208
208
208
208
208
208
208
208
208
208
208
208
208
208
208
208
208
208
208
208
209
209
209
209
209
209
209
209
209
209
HR
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
WS
M/S
1.0
.6
.6
1.2
1.2
1.3
2.0
2.9
1.2
2.1
4.4
5.6
5.4
5.7
4.7
5.0
5.5
6.1
5.6
5.3
4.7
3.8
3.1
2.3
2.5
3.2
3.0
2.5
2.1
2.3
2.7
3.2
3.3
2.5
2.1
2.1
2.6
2.4
1.5
1.9
2.3
2.2
2.0
2.2
2.0
2.0
1.1
.6
.7
.8
1.2
1.2
1.2
1.9
1.4
.4
1.6
2.6
WD
DEC
265.
257.
249.
130.
125.
119.
189.
231.
231.
266.
285.
269.
267.
260.
249.
242.
257.
235.
229.
239.
239.
237.
226.
185.
144.
148.
150.
159.
167.
190.
195.
214.
234.
230.
247.
235.
230.
292.
232.
292.
323.
315.
317.
293.
304.
318.
318.
246.
264.
99.
131.
122.
133.
137.
136.
157.
260.
280.
SOWS
M/S
.247
.161
.164
.179
.126
.108
.441
.582
.484
.536
.866
1.017
1.068
.996
1.120
.991
.976
1.108
1.033
.871
.822
.780
.672
.548
.507
.549
.513
.454
.455
.550
.536
.730
.665
.679
.610
.596
.658
.579
.523
.410
.533
.438
.400
.368
.318
.380
.310
.177
.176
.139
.136
.108
.106
.201
.238
.210
.283
.354
SDWD
DEC
16.2
21.5
17.9
6.3
5.9
4.1
14.6
10.9
32.6
37.2
12.0
10.9
12.2
11.1
16.9
13.7
12.0
10.8
10.4
9.8
9.0
10.2
12.2
15.8
10.2
8.8
8.9
9.2
12.0
13.1
10.7
12.9
13.2
21.5
24.9
19.4
16.4
17.9
27.6
14.9
14.8
13.6
12.5
6.5
9.2
10.6
14.2
14.5
16.0
19.5
8.1
5.3
5.6
6.2
12.6
33.7
11.3
8.5
SDEPA
DEC
30.8
55.1
72.3
10.3
13.4
6.9
51.5
13.6
68.0
51.1
17.7
13.9
16.3
14.1
21.1
21.1
13.4
20.7
12.8
12.0
11.3
11.2
13.7
28.4
10.7
9.2
9.4
10.8
13.4
15.8
11.6
21.7
14.4
27.7
36.5
40.3
28.5
36.8
33.9
23.8
25.3
17.5
20.6
8.9
19.2
20.9
18.4
32.1
31.3
55.4
13.8
10.0
10.9
12.8
18.8
98.8
17.4
9.9
TEMP
°C
17.0
15.7
15.1
13.5
12.5
13.5
15.9
15.8
17.6
20.0
21.1
21.3
21.7
21.7
22.8
23.6
22.5
21.6
20.7
19.3
18.2
17.4
16.9
16.4
15.9
15.6
15.6
15.7
15.7
16.0
16.3
16.9
17.6
18.2
18.8
19.2
19.2
20.7
21.3
20.4
20.7
20.3
20.0
18.1
17.3
16.5
15.4
14.7
14.7
12.6
11.3
10.9
10.3
11.2
13.2
15.1
16.2
17.6
DTDZ
°C
.32
.90
.75
1.42
1.95
.97
-.15
-.41
-.38
-.60
-1.33
-1.52
-1.58
-1.49
-1.50
-1.33
-1.19
-.79
-.51
-.30
-.24
-.17
-.19
-.13
-.05
.02
0.00
-.03
-.06
-.19
-.26
-.40
-.56
-.69
-.73
-.61
-.46
-1.42
-1.42
-.48
-.73
-.35
-.23
-.23
-.12
.13
.32
.33
.38
1.71
2.06
2.00
2.29
.75
-.39
-.54
-.39
-.84
SOLRAD
W/MA2
0.
0.
0.
0.
3.
70.
188.
374.
529.
725.
850.
917.
943.
800.
823.
670.
493.
308.
144.
23.
0.
0.
0.
0.
0.
0.
0.
0.
1.
24.
80.
166.
234.
370.
362.
269.
142.
385.
254.
143.
169.
79.
29.
7.
0.
0.
0.
0.
0.
0.
0.
0.
2.
68.
126.
283.
548.
721.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00.
23

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
209
209
209
209
209
209
209
209
209
209
209
209
209
209
210
210
210
210
210
210
210
210
210
210
210
210
210
210
210
210
210
210
210
210
210
210
210
210
211
211
211
211
211
211
211
211
211
211
211
211
211
211
211
211
211
211
211
211
HR
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
WS
M/S
3.2
4.0
4.2
3.9
4.0
3.4
3.1
2.4
2.4
1.7
4.1
3.4
1.6
1.2
.6
.4
.7
.6
1.5
1.5
1.4
.9
1.6
1.6
1.2
1.9
3.1
3.8
3.9
3.2
3.5
3.7
5.0
4.3
3.4
2.7
3.0
3.9
3.0
2.3
1.6
1.7
2.0
1.9
1.7
2.0
3.0
2.2
1.3
1.2
1.4
1.5
1.3
1.9
1.3
1.5
1.2
1.2
WD
DEC
280.
292.
290.
287.
285.
284.
284.
295.
202.
324.
141.
302.
313.
325.
230.
66.
244.
127.
140.
139.
228.
249.
283.
284.
252.
269.
293.
296.
301.
266.
294.
290.
245.
250.
266.
261.
238.
247.
234.
256.
195.
142.
145.
151.
155.
231.
254.
250.
254.
208.
176.
245.
240.
242.
266.
182.
120.
195.
SOWS
M/S
.426
.447
.521
.626
.580
.478
.447
.648
.533
.536
1.156
.680
.338
.334
.172
.149
.250
.217
.144
.205
.317
.312
.438
.456
.430
.567
.570
.681
.824
.833
.755
.760
.909
.856
.899
.516
.601
.665
.575
.481
.404
.365
.370
.354
.356
.489
.501
.505
.425
.501
.648
.480
.462
.514
.417
.429
.504
.340
SDWD
DEG
9.1
7.0
7.8
10.4
8.5
9.2
8.4
19.4
14.7
23.7
16.3
8.9
10.4
20.6
25.1
38.7
32.6
36.3
5.1
7.2
18.3
31.8
20.7
24.9
30.3
20.8
14.7
13.7
15.3
18.8
14.9
13.5
9.5
10.2
16.6
10.1
13.3
9.2
12.7
12.4
20.9
12.2
11.1
9.8
11.6
11.9
11.1
13.7
25.8
36.3
33.2
34.6
29.5
17.1
19.7
23.2
28.4
23.2
SDEPA
DEG
9.7
7.4
8.5
11.5
9.4
11.6
9.4
31.7
20.9
28.3
30.0
14.3
17.9
25.4
35.8
51.2
60.6
63.9
12.4
14.0
52.6
46.0
29.3
35.6
48.4
26.9
16.5
16.2
25.1
24.6
19.4
23.1
10.4
11.8
21.9
14.1
16.0
12.6
33.4
32.1
57.2
22.4
20.5
12.6
20.3
18.2
15.7
19.6
36.8
82.2
56.3
55.2
73.3
34.4
41.8
58.0
47.6
48.0
TEMP
°C
19.2
20.3
21.8
22.7
23.5
24.2
24.5
25.7
25.3
21.6
19.3
17.7
16.8
15.8
13.5
12.6
13.6
12.2
11.3
13.2
14.7
15.5
16.1
17.1
19.3
20.6
21.8
23.2
23.9
24.0
24.3
24.0
21.7
20.6
19.6
19.0
18.6
17.9
17.3
17.2
16.2
15.3
15.0
15.1
15.5
16.4
16.8
17.6
18.8
21.1
21.7
22.1
21.9
21.7
22.0
24.0
24.6
21.5
DTDZ
°C
-1.09
-1.25
-1.33
-1.38
-1.33
-1.32
-1.19
-2.03
-2.22
-.45
-.03
.01
.15
.35
1.81
1.93
1.07
1.71
1.45
.02
-.30
-.37
-.48
-.62
-1.19
-1.11
-1.24
-1.39
-1.42
-1.30
-1.17
-.96
-.36
-.23
-.23
-.22
-.21
-.26
-.17
-.19
.13
.13
.11
.09
-.04
-.24
-.40
-.62
-.77
-1.58
-1.26
-1.14
-.71
-.44
-.45
-2.16
-2.56
-.77
SOLRAD
W/M"-2
842.
910.
927.
889.
795.
661.
504.
314.
147.
19.
0.
0.
0.
0.
0.
0.
0.
0.
1.
17.
44.
89.
170.
386.
828.
902.
914.
858.
707.
622.
512.
283.
30.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
22.
63.
110.
200.
358.
532.
662.
517.
306.
180.
145.
195.
325.
204.
38.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.02
.02
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
24

-------
YEAR DAY HR   WS  WD   SDWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG     M/S    PEG  PEG    °C    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
211
211
211
211
212
212
212
212
212
212
212
212
212
212
212
212
212
212
212
212
212
212
212
212
212
212
212
212
213
213
213
213
213
213
213
213
213
213
213
213
213
213
213
213
213
213
213
213
213
213
213
213
214
214
214
214
214
214
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
3.1
2.6
2.0
1.7
1.9
1.3
1.2
1.6
1.6
.8
1.0
1.1
.9
1.2
2.1
1.9
1.8
2.2
3.7
4.7
5.1
3.0
1.6
1.9
1.1
1.8
1.9
1.3
2.4
1.9
1.6
1.7
1.5
.7
1.5
1.9
2.0
2.8
2.8
1.7
1.5
2.3
1.3
2.6
4.1
1.3
1.2
.8
.8
1.3
1.0
1.5
1.5
1.3
1.4
1.8
1.7
1.6
263.
319.
300.
234.
201.
208.
175.
279.
318.
144.
176.
281.
295.
106.
124.
128.
147.
208.
224.
240.
223.
252.
249.
286.
283.
251.
239.
197.
156.
126.
119.
122.
133.
126.
122.
136.
167.
199.
261.
269.
307.
217.
146.
207.
142.
108.
96.
131.
271.
166.
79.
141.
142.
155.
142.
142.
142.
118.
.798
.600
.601
.647
.489
.363
.370
.337
.388
.195
.267
.275
.266
.363
.427
.372
.350
.510
.875
.951
.918
.544
.505
.428
.288
.386
.527
.360
.493
.409
.249
.240
.241
.160
.253
.470
.550
.745
.587
.449
.460
.718
.542
.900
.743
.296
.257
.215
.311
.339
.194
.302
.238
.268
.227
.258
.265
.191
13.4
13.8
22.0
32.9
19.7
20.1
28.3
12.4
19.5
21.9
16.8
19.0
22.5
25.6
12.9
13.3
13.0
16.6
11.8
12.8
10.6
10.3
17.1
16.7
19.1
16.9
14.9
21.4
14.4
12.3
7.9
8.7
8.7
19.1
8.9
15.2
18.5
17.7
12.6
20.7
24.1
19.1
38.3
36.3
9.4
31.6
12.1
36.2
29.2
19.1
13.0
14.7
8.5
20.4
19.7
7.1
8.8
5.9
17.2
19.7
33.4
82.3
70.2
53.6
91.2
25.6
26.1
40.4
51.3
31.0
35.6
43.0
18.0
24.8
16.3
27.5
25.6
19.7
11.8
20.7
40.0
32.4
35.0
21.9
22.7
36.0
15.7
24.3
12.8
13.3
13.2
37.0
21.3
21.2
26.9
27.0
25.6
54.0
34.6
94.6
66.2
77.8
10.8
49.1
18.7
68.1
71.7
58.1
39.2
29.0
17.5
34.8
22.0
10.6
19.8
13.7
18.1
17.0
16.4
15.8
15.9
15.5
15.0
14.8
14.2
14.0
14.9
15.6
16.4
17.4
17.1
17.4
17.9
19.0
19.2
18.6
17.6
17.3
18.3
17.1
15.3
16.0
15.8
15.1
14.5
13.0
11.6
11.4
11.6
11.4
13.4
15.6
16.8
18.2
17.5
18.3
19.4
18.8
22.7
20.6
15.6
15.8
16.9
15.1
15.0
14.1
11.9
12.4
11.6
10.9
10.1
9.7
9.1
8.9
-.23
-.11
-.02
.06
-.05
.12
.30
.15
.17
.39
-.18
-.27
-.45
-.90
-.56
-.46
-.35
-.28
-.31
-.41
-.40
-.44
-.64
-.20
.49
.01
-.01
.08
.12
.76
1.71
1.75
1.33
1.54
.23
-.48
-.45
-.74
-.49
-.73
-.90
-1.15
-3.25
-1.06
.16
-.22
-.69
.97
1.04
1.07
2.27
.53
.59
.56
1.02
.60
.54
.78
0.
0.
0.
0.
0.
0.
0.
0.
1.
25.
89.
115.
133.
171.
80.
89.
121.
117.
181.
208.
170.
141.
151.
26.
0.
0.
0.
0.
0.
0.
0.
0.
1.
26.
199.
398.
303.
580.
151.
266.
358.
228.
825.
300.
55.
131.
87.
8.
0.
0.
0.
0.
0.
0.
0.
0.
1.
66.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.07
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                       25

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S   PEG  PEG    °C    °C   W/M~2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
214
214
214
214
214
214
214
214
214
214
214
214
214
214
214
214
214
214
215
215
215
215
215
215
215
215
215
215
215
215
215
215
215
215
215
215
215
215
215
215
215
215
216
216
216
216
216
216
216
216
216
216
216
216
216
216
216
216
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
1.7
1.7
1.9
3.1
4.3
4.6
4.9
4.4
4.5
4.3
3.3
3.7
3.6
3.5
3.4
1.6
2.3
1.4
1.4
1.9
1.7
1.8
1.2
.7
1.0
1.0
1.4
1.0
1.0
1.1
1.3
2.0
2.1
2.3
3.0
2.7
2.7
2.9
1.5
1.9
2.0
2.0
1.7
2.1
1.6
1.6
1.6
1.5
1.2
1.7
2.7
4.2
4.1
4.2
3.8
3.5
3.2
2.9
120.
117.
142.
198.
233.
234.
248.
253.
260.
257.
272.
258.
258.
252.
245.
234.
227.
191.
210.
188.
220.
240.
226.
193.
152.
291.
267.
272.
270.
245.
255.
272.
145.
206.
269.
239.
8.
123.
309.
297.
310.
312.
308.
314.
330.
334.
283.
291.
174.
285.
319.
288.
289.
290.
298.
314.
259.
253.
.300
.375
.504
.727
1.100
.956
.848
.941
.846
.767
.637
.700
.731
.717
.628
.378
.493
.354
.354
.485
.464
.338
.245
.233
.234
.295
.320
.274
.437
.446
.489
.476
.675
.619
.639
.643
.485
.648
.475
.504
.343
.403
.402
.329
.405
.317
.323
.392
.433
.508
.512
.525
.505
.522
.719
.866
.938
.772
10.4
13.9
16.9
13.6
13.7
10.2
10.7
11.6
10.9
10.0
14.3
11.8
11.3
10.6
7.9
11.6
14.2
18.7
14.0
13.8
13.6
10.3
11.5
22.0
22.0
21.4
20.3
19.6
33.5
44.6
26.4
22.2
32.8
23.4
16.0
14.3
10.1
12.9
22.1
14.6
10.8
13.8
17.5
9.6
14.3
12.0
14.1
19.0
25.8
18.1
14.7
7.4
7.7
8.8
16.1
17.0
20.3
16.7
17.8
19.6
20.8
45.0
15.9
14.8
14.5
15.1
12.7
15.7
17.3
13.3
13.1
13.3
8.9
18.5
16.2
29.7
14.7
19.1
27.8
16.5
19.7
73.8
52.6
52.9
33.2
25.2
45.0
58.7
31.6
31.2
88.2
63.5
29.9
18.5
10.4
13.9
29.7
15.5
11.9
15.5
23.9
17.6
18.2
15.5
25.2
20.5
44.5
24.7
28.6
9.0
8.8
9.2
21.7
25.0
24.0
30.4
11.4
14.1
16.5
18.8
20.0
20.0
20.0
20.5
20.3
20.1
19.8
19.5
18.8
18.0
17.5
17.3
17.1
16.5
16.3
16.2
16.0
15.0
14.8
14.7
15.3
16.1
16.5
17.4
18.8
20.5
22.0
22.4
24.2
23.4
23.7
22.9
21.2
19.9
18.9
17.9
17.3
16.9
16.3
15.9
15.6
15.3
14.8
14.5
14.9
15.8
16.2
16.7
17.8
20.0
21.9
23.5
25.9
26.1
-.01
-.44
-.50
-.59
-.68
-.44
-.50
-.64
-.52
-.36
-.27
-.19
-.13
-.19
-.08
.02
.01
.05
-.05
-.07
-.09
-.09
-.09
-.14
-.24
-.47
-.38
-.49
-.70
-1.16
-1.18
-1.10
-2.56
-1.38
-1.38
-1.25
-.68
-.25
-.17
-.15
-.04
.00
.06
-.10
-.13
-.08
-.05
-.11
-.32
-1.03
-1.06
-1.03
-1.15
-1.39
-1.49
-1.63
-3.28
-2.79
224.
399.
565.
518.
530.
271.
364.
427.
240.
197.
82.
52.
23.
7.
0.
0.
0.
0.
0.
0.
0.
0.
0.
9.
65.
138.
130.
325.
532.
653.
782.
583.
584.
366.
338.
143.
48.
5.
0.
0.
0.
0.
0.
0.
0.
0.
1.
36.
150.
205.
422.
714.
828.
898.
908.
874.
784.
645.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      26

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S DEG    M/S   DEG  DEG    °C    °C   W/M^2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
219
219
219
219
219
219
219
219
219
219
219
219
219
219
219
219
219
219
219
219
219
219
220
220
220
220
220
220
220
220
220
220
220
220
220
220
220
220
220
220
220
220
220
220
220
220
221
221
221
221
221
221
221
221
221
221
221
221
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
1.4
.6
.6
.7
1.2
2.0
2.2
3.0
3.4
3.4
4.3
3.8
3.5
3.2
3.1
3.5
4.7
2.9
1.3
2.2
1.6
1.6
1.4
1.1
.4
.7
.6
.5
.6
1.0
1.2
1.9
1.8
2.6
2.3
2.7
2.7
1.7
2.3
1.5
1.6
3.0
3.5
2.9
3.4
3.9
3.2
2.5
2.5
2.5
2.4
2.2
2.1
3.2
4.1
3.9
4.5
5.0
309.
140.
161.
317.
278.
279.
282.
288.
317.
156.
41.
45.
68.
69.
342.
314.
150.
154.
294.
302.
328.
325.
277.
179.
129.
151.
90.
163.
125.
157.
137.
135.
181.
278.
269.
261.
283.
274.
279.
292.
275.
293.
297.
258.
243.
249.
246.
204.
225.
202.
172.
167.
159.
184.
204.
205.
214.
218.
.287
.176
.184
.218
.195
.230
.299
.392
.810
.904
1.251
1.123
.982
.859
.752
.782
1.056
.878
.379
.392
.327
.388
.353
.209
.122
.121
.136
.150
.224
.255
.315
.439
.374
.354
.549
.732
.459
.407
.408
.321
.335
.344
.503
.461
.544
.706
.585
.542
.697
.555
.464
.443
.508
.808
.917
.932
.968
1.008
16.0
19.0
26.3
19.2
10.3
6.9
8.2
7.7
16.6
18.4
16.7
17.2
17.9
19.3
14.7
13.5
11.6
15.0
21.7
11.0
13.7
13.8
23.8
11.6
25.3
14.8
20.4
13.6
21.7
27.7
16.2
15.2
17.3
9.4
13.7
20.0
12.7
18.0
12.8
20.9
16.3
5.5
6.7
9.0
8.7
9.4
12.1
12.2
15.7
12.2
10.6
11.4
13.1
14.0
13.0
13.2
14.1
15.3
23.8
76.9
87.3
26.2
16.0
8.5
8.4
8.6
34.5
24.4
19.4
20.3
21.0
21.2
16.0
15.8
12.9
40.8
32.3
21.2
21.9
17.5
37.9
46.1
72.5
70.6
60.0
26.3
34.3
35.6
25.6
23.9
29.8
17.1
16.7
40.0
19.5
29.9
16.1
37.2
32.9
6.9
7.2
15.0
10.5
15.4
20.7
15.5
18.9
22.7
12.8
13.2
14.5
17.5
14.6
15.2
20.1
19.7
16.1
14.8
14.3
15.0
16.0
17.1
18.7
19.7
23.2
26.8
28.3
29.9
30.6
31.3
29.6
28.4
25.5
23.0
21.5
19.8
18.8
17.4
16.5
15.5
13.9
12.6
12.6
13.3
15.1
16.4
17.4
19.3
20.9
21.4
23.0
25.8
25.2
27.1
27.1
27.7
27.1
24.0
21.5
19.7
17.9
16.6
16.0
15.3
14.9
14.7
14.2
14.3
14.9
16.1
16.9
17.6
18.6
20.0
.10
.89
1.05
.34
-.11
-.34
-.62
-.90
-1.59
-3.50
-4.12
-4.72
-4.86
-4.79
-2.84
-2.30
-1.57
-.24
.20
.26
.26
.17
.51
.88
1.53
2.34
1.90
.91
.25
-.17
-.66
-1.05
-.76
-.83
-1.12
-2.36
-1.10
-1.47
-1.16
-1.12
-.68
-.20
-.10
-.15
-.14
-.17
-.13
-.11
-.13
-.09
-.03
-.14
-.31
-.31
-.41
-.51
-.69
-1.01
0.
0.
0.
44.
192.
369.
536.
693.
812.
880.
898.
859.
769.
634.
467.
282.
112.
11.
0.
0.
0.
0.
0.
0.
0.
0.
1.
45.
180.
206.
189.
496.
542.
410.
706.
848.
558.
617.
450.
288.
146.
15.
0.
0.
0.
0.
0.
0.
0.
0.
0.
19.
86.
126.
172.
267.
408.
754.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      28

-------
YEAR DAY HR   WS  WD
             M/S PEG
SDWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
 M/S   PEG  PEG    °C    °C   W/M"2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
223
223
224
224
224
224
224
224
224
224
224
224
224
224
224
224
224
224
224
224
224
224
224
224
224
224
225
225
225
225
225
225
225
225
225
225
225
225
225
225
225
225
225
225
225
225
225
225
225
225
226
226
226
226
226
226
226
226
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
1.3
1.3
1.0
.6
1.2
1.2
1.4
1.6
1.1
1.1
.8
1.8
2.1
3.1
2.9
2.5
2.4
1.7
2.1
2.7
3.7
3.4
1.6
2.5
2.1
1.8
.9
1.2
.8
1.2
1.6
1.8
1.6
1.6
1.4
2.5
3.1
3.2
3.5
3.5
3.3
3.8
3.3
4.1
3.1
2.7
3.3
2.9
1.5
2.1
2.1
1.2
1.5
1.9
2.1
1.8
2.0
1.9
272.
293.
312.
203.
127.
133.
144.
144.
135.
139.
220.
275.
275.
288.
290.
286.
280.
208.
126.
143.
234.
264.
258.
250.
234.
170.
187.
141.
139.
153.
132.
138.
126.
136.
133.
243.
289.
302.
313.
295.
298.
285.
270.
295.
291.
286.
295.
261.
293.
285.
245.
274.
291.
247.
247.
188.
158.
186.
.551
.386
.272
.244
.241
.162
.139
.170
.200
.253
.242
.255
.338
.436
.542
.577
.540
.392
.422
.492
.725
.714
.625
.589
.460
.417
.202
.182
.161
.279
.255
.205
.221
.348
.568
.592
.611
.607
.803
.722
.875
.825
.730
.632
.501
.518
.576
.624
.416
.373
.307
.254
.221
.403
.389
.419
.448
.577
39.5
20.6
21.2
41.7
22.3
7.7
4.4
4.1
9.2
16.7
18.6
9.5
11.4
9.9
14.9
17.1
13.5
14.1
11.7
10.7
12.6
13.8
30.3
14.0
11.3
15.8
19.4
9.4
14.2
11.8
12.1
6.3
8.5
12.4
26.7
25.5
10.1
14.0
13.9
13.0
19.1
14.1
14.0
7.9
9.5
11.3
9.8
11.1
15.0
9.3
8.5
22.2
7.4
13.8
12.0
12.3
12.5
20.2
52.4
24.7
24.7
78.4
28.0
13.8
6.5
7.9
14.0
32.5
32.1
23.3
14.3
12.2
20.3
22.6
20.3
56.0
20.8
21.0
28.3
15.7
36.2
15.5
17.5
19.9
35.8
22.5
37.9
65.8
34.1
8.1
16.6
19.0
37.5
67.0
11.1
20.6
23.8
34.3
41.3
18.0
17.1
8.3
12.3
17.0
10.8
12.3
35.8
29.3
11.3
37.5
10.2
26.8
18.5
41.9
13.5
23.0
16.9
16.4
15.6
13.8
11.3
10.9
10.1
9.8
11.1
12.6
14.9
16.4
18.1
19.8
22.5
23.3
21.8
22.3
23.0
23.1
22.6
20.9
19.3
18.5
17.6
17.1
16.5
15.1
14.8
14.6
13.9
13.8
14.4
16.5
19.0
20.5
21.4
21.9
23.0
22.9
24.5
24.3
24.1
22.8
22.0
20.7
19.9
19.3
18.6
18.2
17.7
17.5
16.9
16.9
16.5
16.3
16.5
17.5
.06
.13
.38
1.02
1.84
1.63
1.66
1.37
.13
-.36
-.26
-.52
-.90
-1.05
-1.30
-.90
-.10
-.22
-.68
-.54
-.25
.03
.13
-.07
.00
.17
.46
.93
.73
1.09
1.28
1.18
.35
-.26
-.57
-.83
-1.04
-.88
-1.41
-1.34
-1.83
-1.26
-1.15
-.62
-.30
-.13
-.21
-.18
-.13
-.17
-.14
-.07
-.11
-.13
-.09
-.02
-.11
-.39
0.
0.
0.
0.
0.
0.
0.
21.
77.
198.
433.
310.
646.
858.
888.
381.
109.
158.
206.
183.
99.
5.
0.
0.
0.
0.
0.
0.
0.
0.
0.
16.
95.
243.
557.
648.
738.
461.
695.
532.
769.
622.
403.
175.
56.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
14.
175.
216.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      30

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
226
226
226
226
226
226
226
226
226
226
226
226
226
226
226
226
227
227
227
227
227
227
227
227
227
227
227
227
227
227
227
227
227
227
227
227
227
227
227
227
228
228
228
228
228
228
228
228
228
228
228
228
228
228
228
228
228
228
HR
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
WS
M/S
2.9
2.9
2.9
3.8
3.6
4.6
4.4
6.2
5.8
2.7
1.1
1.2
1.0
1.6
.7
.4
1.4
2.3
2.3
2.2
1.1
.8
1.1
1.2
2.7
2.4
3.3
3.4
3.3
3.1
2.4
2.0
2.7
3.0
2.1
4.6
4.0
2.6
2.5
2.0
2.0
2.5
2.3
2.2
1.9
2.5
2.5
2.4
2.4
2.0
1.9
2.2
1.9
1.6
1.2
2.5
1.9
.9
WD
DEC
230.
247.
213.
239.
235.
273.
286.
151.
14.
173.
257.
277.
294.
313.
275.
155.
116.
146.
145.
155.
133.
94.
228.
208.
244.
299.
300.
309.
298.
284.
284.
308.
310.
281.
263.
246.
256.
241.
201.
180.
177.
165.
164.
174.
181.
184.
185.
180.
177.
212.
231.
224.
192.
131.
153.
188.
169.
130.
SDWS
M/S
.721
.704
.622
.809
1.056
.882
1.051
1.351
1.594
1.049
.426
.312
.243
.262
.209
.148
.179
.264
.318
.313
.242
.259
.327
.396
.545
.450
.563
.679
.601
.519
.563
.559
.637
.575
.461
.886
.808
.537
.556
.464
.538
.555
.399
.463
.505
.566
.549
.530
.479
.509
.450
.534
.506
.480
.401
.564
.406
.202
SDWD
DEC
15.3
12.8
16.2
12.1
17.4
12.7
16.4
13.9
14.9
20.9
35.4
16.2
24.2
9.6
24.4
21.5
6.5
5.8
6.1
7.5
12.3
30.9
22.1
21.7
11.7
12.4
14.7
15.9
13.5
11.7
19.1
31.4
20.2
12.3
18.8
9.3
11.3
11.3
12.0
11.6
14.4
12.0
11.5
10.4
14.8
12.2
12.4
12.1
11.8
16.4
15.8
15.0
20.0
21.0
25.1
12.2
12.8
13.4
SDEPA
DEC
28.8
17.9
31.6
15.1
22.2
17.9
28.2
14.9
18.2
27.2
56.7
58.0
46.2
18.0
49.3
76.6
13.6
9.3
8.0
10.6
17.4
38.8
48.1
32.4
18.5
15.9
19.6
23.6
14.7
13.2
25.1
39.2
29.2
16.6
30.2
11.8
14.6
16.6
30.7
13.5
15.7
14.9
17.7
11.2
16.9
12.7
13.5
13.5
17-7
28.7
23.9
23.7
50.0
40.3
35.2
18.1
22.3
25.9
TEMP
°C
18.3
18.3
19.6
19.9
22.1
22.4
21.2
21.1
18.2
17.4
16.3
15.4
15.0
14.6
14.6
14.4
13.4
13.6
13.6
13.2
11.5
12.0
13.9
14.7
15.1
15.6
17.1
18.5
19.5
21.1
22.2
22.8
23.3
21.3
20.9
19.8
18.1
17.1
16.2
15.4
14.9
14.7
14.8
15.1
15.3
15.5
15.8
16.1
16.5
17.1
17.9
18.5
19.4
20.0
19.8
19.1
18.8
19.0
DTDZ
°C
-.50
-.33
-.82
-.59
-1.27
-1.17
-2.29
-3.27
-1.94
-1.04
-.33
-.11
-.08
-.01
.07
.56
1.03
.61
.23
.23
1.43
.84
-.14
-.25
-.38
-.65
-1.03
-1.53
-1.11
-1.25
-1.42
-1.35
-1.60
-.54
-.23
-.14
-.10
-.05
.05
-.02
-.04
-.12
-.13
-.18
-.14
-.16
-.17
-.21
-.28
-.31
-.47
-.43
-.65
-1.02
-.54
-.29
-.33
-.35
SOLRAD
211.
125.
509.
263.
854.
572.
448.
530.
259.
133.
32.
1.
0.
0.
0.
0'.
0.
0.
0.
0.
0.
12.
48.
96.
109.
451.
822.
828.
765.
815.
747.
444.
383.
97.
30.
4.
0.
0.
0.
0.
0.
0.
0.
0.
0.
4.
26.
52.
73.
84.
173.
174.
281.
213.
148.
78.
92.
46.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00'
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
31

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
231
231
231
231
231
231
231
231
231
231
231
231
231
231
231
231
231
231
231
231
232
232
232
232
232
232
232
232
232
232
232
232
232
232
232
232
232
232
232
232
232
232
232
232
233
233
233
233
233
233
233
233
233
233
233
233
233
233
HR
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
WS
M/S
1.8
2.2
2.5
2.0
2.3
2.8
2.7
2.2
2.6
2.1
2.1
1.8
2.3
2.2
2.3
2.3
2.7
3.3
2.8
3.3
2.5
2.8
2.0
1.9
2.0
1.9
2.0
1.8
2.3
2.4
2.5
3.1
3.2
3.4
5.4
5.0
5.8
6.2
5.6
3.9
2.2
2.4
2.9
2.4
2.9
4.0
3.9
4.2
4.3
3.1
2.5
3.5
3.6
3.9
4.8
5.0
4.9
5.0
WD
DEC
196.
249.
178.
191.
188.
189.
195.
168.
216.
282.
220.
190.
156.
148.
138.
126.
194.
253.
256.
246.
255.
254.
257.
218.
226.
256.
241.
232.
225.
238.
252.
222.
230.
254.
253.
220.
240.
238.
218.
208.
174.
185.
194.
180.
180.
192.
195.
202.
196.
182.
173.
191.
203.
211.
229.
233.
247.
198.
SDWS
M/S
.439
.446
.508
.470
.507
.590
.568
.632
.602
.526
.547
.450
.470
.453
.429
.327
.503
.479
.466
.571
.478
.446
.311
.332
.353
.309
.319
.351
.596
.559
.599
.881
.842
.824
.926
1.228
1.060
1.077
1.029
.827
.652
.646
.714
.631
.755
1.086
1.239
1.355
1.184
.890
.674
.811
.946
1.006
1.060
.965
.935
1.190
SDWD
DEC
17.0
10.6
11.4
16.0
11.4
10.8
13.5
18.1
14.1
15.7
16.9
17.4
13.6
12.0
9.6
6.7
11.5
8.3
10.3
9.5
9.9
9.2
8.1
8.9
9.4
10.0
8.7
10.2
12.9
13.5
14.1
19.6
17.9
16.5
10.8
13.9
10.7
10.0
10.7
13.2
16.3
13.0
12.9
13.6
15.1
13.6
17.5
16.5
14.2
17.3
16.6
13.7
15.7
15.7
11.4
12.1
11.1
11.4
SDEPA
DEC
26.7
16.9
26.2
19.6
14.6
16.0
17.4
21.6
20.3
21.8
24.1
33.1
16.1
15.4
12.4
7.5
59.0
10.4
13.0
12.8
13.8
12.0
8.6
31.0
15.6
16.8
11.6
19.1
18.4
17.5
24.5
24.0
25.8
20.6
11.9
20.1
24.3
17.3
12.6
22.1
18.5
15.0
16.3
16.6
17.6
15.9
18.9
17.0
15.5
20.1
20.7
15.1
18.9
24.5
20.7
17.4
13.0
20.4
TEMP
°C
15.8
15.9
15.6
15.8
16.3
16.7
17.7
18.8
19.2
19.4
19.6
19.9
20.2
20.3
20.0
19.5
19.1
18.1
17.6
17.2
17.0
16.9
16.8
16.6
16.5
16.2
16.1
16.4
17.2
18.0
19.0
20.8
21.8
22.3
21.7
21.7
21.1
19.9
19.1
18.1
17.2
17.4
17.5
16.9
16.9
17.4
17.6
17.6
17.4
17.4
17.6
18.3
19.1
20.1
20.8
21.7
22.0
20.2
DTDZ
°C
-.22
-.23
-.24
-.31
-.35
-.40
-.58
-.71
-.63
-.60
-.49
-.41
-.40
-.34
-.16
-.10
-.14
-.19
-.19
-.18
-.17
-.19
-.18
-.16
-.19
-.19
-.26
-.27
-.43
-.56
-.69
-.97
-.85
-.82
-.79
-.59
-.57
-.41
-.20
-.05
0.00
-.03
-.05
-.09
-.07
-.06
-.07
-.08
-.05
-.08
-.18
-.31
-.41
-.49
-.61
-.76
-.82
-.43
SOLRAD
W/M~2
0.
4.
36.
65.
89.
143.
305.
287.
250.
245.
138.
120.
99.
66.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
17.
46.
128.
248.
356.
576.
428.
308.
352.
308.
232.
122.
17.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
4.
53.
175.
231.
260.
438.
450.
461.
251.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
33

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
233
233
233
233
233
233
233
233
233
233
234
234
234
234
234
234
234
234
234
234
234
234
234
234
234
234
234
234
234
234
234
234
234
234
235
235
235
235
235
235
235
235
235
235
235
235
235
235
235
235
235
235
235
235
235
235
235
235
HR
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
WS
M/S
4.4
5.1
4.1
5.0
2.2
2.6
2.9
2.2
2.7
2.3
2.9
2.5
1.3
.9
1.4
1.3
1.5
2.0
1.2
1.3
1.7
2.3
2.0
1.8
3.2
5.2
3.4
2.9
2.3
2.5
2.8
1.9
1.6
1.3
1.0
1.1
.5
1.3
1.4
1.8
1.4
1.3
1.8
2.2
1.7
2.1
3.2
2.7
2.5
2.7
3.3
3.7
3.9
3.5
3.1
3.5
3.2
2.0
WD
DEC
183.
216.
232.
287.
266.
181.
148.
155.
174.
172.
196.
235.
208.
127.
276.
274.
130.
158.
206.
292.
291.
279.
275.
266.
308.
300.
319.
295.
283.
245.
248.
326.
307.
308.
310.
292.
156.
275.
300.
293.
303.
314.
286.
293.
306.
301.
279.
279.
285.
289.
289.
292.
267.
251.
252.
242.
245.
214.
SOWS
M/S
1.145
1.215
.894
.938
.557
.676
.578
.453
.565
.488
.711
.588
.371
.228
.354
.257
.304
.401
.388
.509
.395
.508
.459
.669
.710
.816
.687
.528
.391
.406
.651
.433
.406
.300
.246
.265
.187
.226
.244
.300
.199
.285
.376
.427
.477
.559
.500
.520
.510
.634
.612
.621
.666
.640
.567
.597
.595
.461
SDWD
DEC
13.5
12.9
11.6
8.8
18.3
19.2
9.1
11.7
10'. 7
12.1
12.1
13.4
13.7
28.9
19.5
24.2
7.5
12.2
23.6
30.1
17.4
13.9
15.3
29.9
17.1
9.5
11.9
9.7
8.6
7.3
14.1
12.8
13.9
16.3
15.2
11.2
18.4
12.3
9.3
7.9
8.4
14.0
12.9
11.5
22.7
31.2
12.2
11.9
18.0
13.4
8.6
8.5
9.4
9.1
10.9
8.2
8.8
13.6
SDEPA
DEC
14.6
23.9
18.7
21.5
28.2
52.7
11.0
16.7
15.8
14.5
16.2
17.9
34.3
40.5
43.5
55.0
11.7
18.3
59.7
35.0
29.6
15.1
17.4
47.1
23.4
10.8
21.3
12.8
19.3
9.4
33.9
24.8
23.9
23.2
19.1
21.8
79.7
31.8
12.1
9.0
11.4
24.6
15.8
15.7
34.5
46.5
13.2
14.9
21.2
17.9
9.8
9.4
14.3
9.9
14.3
9.3
10.1
36.5
TEMP
°C
21.1
21.8
21.6
18.0
16.4
16.4
15.8
15.7
15.7
15.4
15.6
15.3
14.7
13.6
14.0
13.5
14.0
14.9
16.0
16.8
18.0
19.1
20.1
21.7
21.7
21.1
20.5
20.0
19.8
19.0
17.6
16.7
16.6
15.8
15.2
14.9
14.4
14.8
14.6
14.5
14.7
15.1
15.5
15.8
16.9
19.2
19.4
20.2
21.4
22.0
21.5
21.2
20.1
18.8
17.7
16.6
15.8
15.0
DTDZ
°C
-.46
-.44
-.27
-.07
.54
.25
.09
.08
.10
. .09
.04
.04
.19
.71
.29
.30
-.25
-.32
-.32
-.47
-.81
-.97
-.95
-1.52
-.93
-.82
-.83
-.42
-.26
-.05
-.16
-.03
-.07
.14
.14
-.01
.28
-.11
-.12
-.18
-.20
-.32
-.44
-.40
-.75
-1.35
-1.10
-1.19
-1.32
-1.12
-.70
-.53
-.31
-.11
-.08
-.10
-.06
.09
SOLRAD
W/M^2
253.
238.
89.
14.
6.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
13.
74.
206.
338.
273.
605.
776.
709.
709.
489.
482.
235.
155.
67.
4.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
33.
77.
200.
166.
317.
784.
782.
822.
719.
551.
257.
147.
44.
1.
0.
0.
0.
0.
PCPN
IN
.00
.00
.00
.09
.13
.04
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
34

-------
YEAR DAY HR   WS  WD
SDWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
                   °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
236
236
236
236
236
236
236
236
236
236
236
236
236
236
236
236
236
236
236
236
236
236
236
236
237
237
237
237
237
237
237
237
237
237
237
237
237
237
237
237
237
237
237
237
237
237
237
237
238
238
238
238
238
238
238
238
238
238
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
2.1
1.6
1.4
1.4
1.4
1.3
1.1
2.0
1.5
1.2
1.0
1.0
2.4
3.0
3.1
2.9
2.2
1.1
1.1
1.4
2.1
2.2
1.9
1.8
1.1
1.2
1.6
1.4
.7
.5
.6
1.0
1.5
2.0
3.1
3.6
3.6
4.1
3.9
3.2
2.9
2.0
1.7
1.6
1.1
.7
.9
.7
.8
.8
.9
.6
.7
.6
1.2
1.0
1.4
3.1
158.
152.
123.
130.
138.
110.
150.
148.
128.
133.
128.
252.
282.
301.
298.
296.
300.
289.
154.
131.
202.
301.
312.
296.
175.
125.
121.
127.
90.
102.
135.
214.
269.
281.
281.
285.
279.
286.
286.
149.
101.
181.
314.
297.
213.
131.
302.
202.
164.
164.
139.
183.
164.
123.
136.
188.
262.
279.
.353
.347
.254
.213
.224
.186
.236
.299
.345
.462
.388
.374
.481
.658
.655
.659
.428
.311
.278
.338
.502
.468
.328
.347
.175
.201
.112
.158
.124
.109
.110
.206
.219
.286
.455
.475
.476
.584
.542
.806
.799
.617
.366
.284
.309
.196
.255
.193
.188
.144
.145
.129
.199
.189
.157
.191
.259
.426
*«'•*-"•"'
8.7
11.6
15.3
9.5
8.4
12.1
12.7
8.7
14.3
25.8
26.8
30.0
15.6
15.4
15.7
16.2
14.8
20.0
23.0
14.9
18.0
10.3
9.8
10.4
11.2
13.0
3.8
4.4
10.1
16.1
10.8
20.7
9.4
8.9
8.0
8.8
9.0
8.2
8.5
21.2
18.4
23.7
13.0
11.0
25.7
28.3
14.2
22.3
24.0
12.3
8.0
14.7
21.8
23.1
12.1
18.4
17.2
7.5
10.3
13.1
19.8
16.4
20.4
22.7
45.9
18.5
20.5
38.9
65.7
47.2
18.7
20.7
18.0
19.4
25.3
42.9
83.2
35.7
92.0
12.7
24.4
13.2
48.5
14.7
5.9
7.2
30.3
46.0
29.2
72.6
11.7
9.5
8.4
9.6
10.0
8.8
9.5
50.2
24.8
44.0
20.3
20.2
57.8
62.0
39.7
72.6
77.7
28.8
16.9
36.0
59.6
50.6
16.6
28.0
29.9
8.5
13.8
12.8
11.5
11.2
11.4
10.7
12.6
13.7
15.0
15.7
16.6
17.0
17.2
18.9
19.7
20.0
19.9
20.5
19.8
18.9
18.2
17.1
16.1
15.5
13.7
11.6
11.4
11.8
11.7
11.7
13.0
14.4
15.3
15.9
17.4
19.2
20.4
21.8
22.4
25.0
26.1
24.7
22.6
19.5
18.0
16.5
15.6
14.8
13.9
12.7
12.1
12.5
12.6
11.7
12.5
13.8
15.9
17.8
.23
.37
1.30
1.64
1.12
1.53
.28
-.42
-.81
-.78
-1.03
-.69
-.69
-1.23
-1.13
-.87
-.69
-.80
-.25
.07
-.05
.05
.21
.15
.95
1.59
1.09
.72
.89
1.06
.24
-.26
-.51
-.68
-1.07
-1.26
-1.27
-1.27
-1.18
-2.89
-3.71
-2.26
-.96
.19
.88
.91
.68
1.05
1.37
1.45
1.34
.87
.99
1.51
.23
-.02
-.23
-.92
0.
0.
0.
0.
0.
12.
48.
128.
156.
160.
208.
227 .
444.
763.
648.
441.
170.
125.
26.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
10.
69.
176.
254.
384.
768.
826.
841.
793.
684.
536.
365.
192.
41.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
10.
65.
284.
459.
631.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      35

-------
YEAR DAY HR   WS  WD
             M/S PEG
SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
 M/S   PEG  PEG    °C    °C   W/MA2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
238
238
238
238
238
238
238
238
238
238
238
238
238
238
239
239
239
239
239
239
239
239
239
239
239
239
239
239
239
239
239
239
239
239
239
239
239
239
240
240
240
240
240
240
240
240
240
240
240
240
240
240
240
240
240
240
240
240
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
3.4
3.7
3.4
2.9
2.8
3.4
3.4
2.8
2.5
1.3
1.3
1.1
1.6
1.3
.8
1.6
1.2
1.1
1.4
1.7
1.8
1.5
1.3
1.0
2.3
3.8
3.2
3.1
3.5
3.6
3.4
3.2
2.5
3.1
2.3
1.1
2.5
2.3
2.6
1.8
1.2
1.6
1.8
1.1
1.5
1.5
1.2
2.6
2.1
2.3
3.4
3.6
2.6
2.7
2.9
2.6
2.2
1.5
277.
309.
339.
350.
17.
206.
209.
230.
64.
212.
230.
278.
270.
322.
245.
139.
123.
138.
128.
162.
224.
209.
225.
229.
291.
315.
318.
307.
299.
304.
298.
304.
268.
247.
249.
272.
259.
251.
255.
259.
205.
191.
168.
130.
148.
136.
214.
294.
293.
282.
290.
285.
273.
281.
286.
289.
273.
17.
.369
.769
.868
.836
.879
.902
.843
.688
.585
.502
.267
.274
.341
.344
.238
.273
.183
.166
.141
.268
.346
.361
.339
.369
.481
.706
.657
.625
.526
.628
.469
.554
.397
.447
.368
.311
.369
.419
.492
.351
.397
.393
.398
.261
.356
.439
.290
.414
.370
.408
.509
.468
.347
.331
.355
.342
.320
.456
7.0
15.6
15.9
18.9
18.4
18.0
15.0
14.7
11.9
22.0
13.5
24.5
14.0
19.4
23.8
8.3
11.2
9.8
6.1
7.9
14.2
16.4
21.1
32.6
14.4
10.7
14.4
14.2
9.1
10.9
8.6
9.6
10.2
7.1
8.6
15.8
10.9
9.9
10.3
11.4
24.2
16.1
11.4
14.8
18.5
17.6
15.9
9.2
14.2
10.8
11.6
8.0
7.9
8.9
7.0
8.6
7.9
19.4
7.6
30.9
17.5
20.3
21.0
20.8
17.5
21.7
17.0
43.1
34.8
45.1
25.6
36.9
47.1
20.0
20.6
27.5
15.7
11.1
27.9
33.2
46.7
65.9
24.0
12.3
19.1
19.9
9.9
14.6
10.4
10.8
19.2
9.7
12.7
28.9
14.2
15.2
12.1
15.3
31.2
27.2
21.8
26.6
23.2
22.6
50.8
14.3
27.6
15.5
12.0
8.5
8.6
9.1
9.4
10.8
24.9
22.2
19.1
21.7
23.6
25.4
28.4
27.6
27.5
25.0
22.7
20.7
19.2
17.5
17.1
16.7
15.5
13.7
12.8
12.6
11.8
13.2
13.8
13.7
14.3
15.5
16.9
17.8
20.0
21.8
22.9
22.7
21.7
20.9
20.3
18.6
17.3
16.4
15.9
15.3
15.1
15.1
15.1
15.0
14.8
14.9
15.0
15.2
15.2
15.6
16.4
17.2
18.2
19.1
20.2
20.8
20.4
20.4
18.8
17.1
-1.13
-1.58
-2.40
-3.17
-5.02
-3.48
-3.51
-1.48
-.53
.23
.41
.41
.69
.43
.73
.92
1.19
1.10
1.47
.17
-.24
-.33
-.43
-.55
-.92
-1.36
-1.57
-1.38
-1.18
-.85
-.69
-.46
-.28
-.13
-.05
.13
-.03
-.04
-.20
-.21
-.16
-.17
-.17
-.23
-.24
-.39
-.32
-.53
-.81
-.88
-1.19
-1.26
-1.15
-.94
-.79
-.72
-.33
.41
749.
817.
829.
785.
689.
553.
361.
130.
23.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
23.
53.
114.
235.
670.
815.
825.
782.
707.
318.
174.
140.
28.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
16.
49.
62.
212.
321.
548.
801.
733.
515.
384.
248.
213.
38.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      36

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
240
240
240
240
241
241
241
241
241
241
241
241
241
241
241
241
241
241
241
241
241
241
241
241
241
241
241
241
242
242
242
242
242
242
242
242
242
242
242
242
242
242
242
242
242
242
242
242
242
242
242
242
243
243
243
243
243
243
HR
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
WS
M/S
1.1
1.0
1.0
1.2
1.5
1.3
.6
1.2
1.6
1.7
1.6
2.0
1.9
1.3
2.9
3.3
3.6
3.1
3.1
2.8
2.5
2.3
1.5
1.7
.9
.7
.7
.8
.8
2.8
3.4
3.4
3.9
3.5
3.3
2.5
2.6
3.8
4.1
4.1
3.5
2.9
4.3
5.2
6.0
5.1
3.8
3.3
2.7
3.0
2.5
3.1
3.4
2.8
1.9
1.6
1.4
1.9
WD
DEC
247.
209,
52.
35.
110.
220.
241.
55.
42.
96.
176.
210.
161.
96.
279.
156.
123.
182.
294.
237.
275.
293.
310.
271.
101.
111.
103.
177.
146.
253.
248.
236.
228.
220.
230.
244.
207.
201.
221.
231.
226.
247.
259.
261.
253.
262.
257.
244.
224.
221.
210.
223.
233.
212.
157.
141.
128.
149.
SDWS
M/S
.370
.444
.367
.393
.454
.436
.275
.504
.565
.494
.482
.498
.514
.546
.400
.840
.910
.814
.628
.702
.709
.714
.541
.232
.225
.129
.200
.174
.163
.537
.592
.703
.837
.738
.684
.501
.646
.918
.904
.751
.710
.696
.984
.985
1.092
.843
.673
.604
.561
.669
.543
.610
.555
.639
.412
.369
.322
.353
SDWD
DEG
28.8
34.0
36.8
28.2
18.1
30.1
36.1
26.3
16.5
17.1
16.4
16.4
18.7
26.1
9.0
17.1
17.1
, 19.4
14.9
14.1
21.4
24.7
26.8
8.1
22.0
8.9
21.2
21.4
13.4
11.6
10.3
11.5
11.7
11.3
12.0
12.6
17.3
13.9
11.4
11.1
15.4
12.5
10.9
12.2
9.9
10.0
9.4
8.9
11.0
11.3
12.6
10.1
9.2
15.2
12.0
14.0
12.5
11.7
SDEPA
DEG
48.5
42.8
50.8
34.3
27.6
40.0
72.0
44.6
20.6
22.5
18.9
18.8
26.1
44.7
11.5
44.8
23.2
32.5
25.6
20.5
32.4
27.3
37.2
29.6
31.9
41.4
78.7
74.9
28.3
14.3
15.1
14.9
14.3
14.0
19.5
14.8
23.6
18.0
14.7
13.9
26.6
14.6
13.4
14.8
11.2
11.6
11.4
9.8
13.3
13.8
14.8
12.8
10.7
24.8
13.3
16.8
13.9
31.2
TEMP
°C
16.0
15.2
14.3
13.9
13.6
13.5
13.7
13.8
13.6
13.2
13.3
13.4
14.5
17.2
17.2
20.6
22.4
24.0
22.8
24.0
22.7
21.8
20.9
18.8
15.6
15.2
14.5
14.3
12.7
14.7
14.3
14.5
14.9
14.9
14.8
14.6
15.4
16.2
16.9
17.4
18.0
18.4
19.4
20.3
20.1
19.4
17.8
16.8
16.5
16.6
16.1
16.0
16.0
16.0
15.3
15.1
15.0
15.1
DTDZ
°C
.35
.52
.72
.74
.54
.14
-.11
-.40
-.52
-.49
-.59
-.88
-1.48
-2.15
-1.00
-3.00
-3.81
-3.97
-1.78
-2.99
-1.28
-.63
-.30
.38
2.22
1.72
1.88
1.02
1.72
-.08
-.23
-.22
-.19
-.16
-.20
-.26
-.26
-.33
-.39
-.37
-.38
-.44
-.68
-1.04
-.84
-..64
-.27
-.03
0.00
-.12
-.09
-.11
-.13
-.09
-.05
.02
.11
.04
SOLRAD
W/M~2
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
25.
47.
155.
459.
740.
812.
825.
784.
495.
377.
208.
159.
29.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
14.
49.
87.
131.
159.
154.
166.
183.
350.
510.
358.
197.
31.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
37

-------
YEAR DAY HR   WS  WD
             M/S PEG
SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
 M/S   PEG  PEG    °C    °C   W/M^2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
243
243
243
243
243
243
243
243
243
243
243
243
243
243
243
243
243
243
244
244
244
244
244
244
244
244
244
244
244
244
244
244
244
244
244
244
244
244
244
244
244
244
245
245
245
245
245
245
245
245
245
245
245
245
245
245
245
245
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
1.4
1.8
2.7
2.1
1.9
2.1
2.5
1.9
2.6
2.5
2.0
1.8
1.6
1.6
1.8
1.6
.8
1.2
.8
.6
.6
1.6
1.1
.5
.6
.8
.4
1.0
1.0
.9
1.6
3.1
2.2
3.1
2.7
2.5
2.7
2.6
2.8
2.4
2.1
1.8
1.8
2.7
2.2
2.8
2.2
1.9
2.1
2.6
3.0
3.2
3.0
2.8
2.3
2.0
2.2
1.6
167.
142.
242.
253.
291.
258.
310.
282.
314.
270.
289.
264.
311.
126.
277.
298.
239.
314.
226.
240.
221.
337.
308.
314.
149.
244.
235.
219.
280.
239.
266.
224.
194.
152.
185.
184.
191.
174.
200.
215.
183.
179.
188.
185.
192.
184.
170.
171.
164.
181.
205.
203.
201.
215.
216.
168.
250.
184.
.359
.374
.521
.550
.539
.545
.637
.546
.591
.546
.415
.420
.409
.388
.460
.455
.289
.247
.209
.189
.211
.315
.285
.163
.136
.159
.204
.315
.269
.325
.384
.742
.544
.644
.605
.506
.524
.548
.620
.456
.523
.475
.488
.522
.502
.565
.463
.433
.424
.550
.655
.805
.802
.801
.577
.586
.626
.620
12.5
12.2
14.1
18.1
24.9
17.3
20.2
27.5
16.1
13.2
13.2
13.6
14.3
15.3
13.4
24.6
20.9
13.0
22.1
26.4
24.5
11.8
10.1
28.5
11.7
12.6
39.0
21.8
24.6
30.2
31.5
14.2
13.6
12.1
13.4
13.1
10.5
11.1
11.5
10.5
12.9
17.2
14.8
10.9
12.4
11.2
11.5
12.3
10.8
11.3
14.6
16.2
17.0
21.3
19.6
24.0
24.0
33.5
26.3
22.2
31.6
23.3
37.3
25.1
27.9
38.2
19.0
20.4
22.5
31.7
21.7
18.7
20.6
48.7
41.4
17.7
64.3
46.8
81.2
15.5
22.1
35.6
39.4
46.3
78.4
49.0
37.2
40.8
44.3
22.3
19.2
18.6
21.9
27.7
22.0
12.6
15.6
16.9
15.8
24.6
16.7
12.3
16.5
12.3
13.0
13.2
16.6
16.0
23.5
20.3
27.6
30.1
37.6
70.1
30.7
74.4
15.5
16.1
16.4
17.2
17.8
18.6
19.1
19.4
19.6
19.6
19.2
19.1
18.5
16.8
16.0
15.6
14.6
14.4
14.5
14.4
14.2
14.1
13.7
13.4
13.6
14.1
14.8
15.5
16.1
16.6
18.2
15.6
15.4
17.4
17.5
17.5
16.7
16.0
15.4
15.3
14.8
14.6
14.6
14.4
14.2
13.9
13.8
13.9
14.2
14.6
15.8
17.1
18.3
18.8
19.0
20.0
20.8
20.8
-.18
-.43
-.41
-.60
-.64
-.73
-.86
-.72
-.79
-.64
-.45
-.37
-.16
.00
.03
.05
.41
-.03
-.06
-.06
.10
-.13
-.07
.10
.05
-.21
-.33
-.36
-.43
-.39
-.84
-.14
-.17
-1.06
-.57
-.47
-.09
-.06
-.05
-.06
-.08
-.04
-.08
-.09
-.11
-.13
-.08
-.09
-.13
-.27
-.45
-.75
-.88
-.69
-.65
-.99
-.98
-.78
47.
104.
141.
332.
263.
349.
317.
310.
303.
212.
109.
78.
20.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
25.
38.
85.
141.
130.
261.
292.
70.
222.
468.
276.
149.
19.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
29.
117.
368.
571.
573.
348.
250.
317.
483.
147.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.02
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      38

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S DEG    M/S    DEG   DEG    °C    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
250
250
250
250
250
250
250
250
250
250
250
250
251
251
251
251
251
251
251
251
251
251
251
251
251
251
251
251
251
251
251
251
251
251
251
251
252
252
252
252
252
252
252
252
252
252
252
252
252
252
252
252
252
252
252
252
252
252
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
3.4
3.3
2.9
3.1
3.5
3.9
3.2
1.1
1.1
1.1
.6
1.0
1.3
.8
1.3
1.0
1.2
.8
.8
.8
1.2
2.2
2.5
3.6
5.3
6.5
6.9
6.3
6.7
6.7
4.0
3.3
3.5
2.7
1.6
.9
1.2
2.7
4.6
3.9
3.9
4.0
3.2
2.5
2.4
2.4
4.2
5.2
5.0
5.6
5.0
6.1
7.1
6.9
5.9
5.7
2.9
.5
175.
318.
206.
315.
343.
208.
4.
263.
233.
138.
160.
164.
150.
116.
148.
139.
134.
167.
169.
200.
109.
264.
306.
178.
64.
92.
267.
180.
7.
12.
30.
26.
25.
89.
108.
298.
270.
46.
68.
55.
61.
60.
46.
31.
42.
99.
266.
150.
296.
264.
354.
325.
6.
11.
13.
12.
30.
255.
.840
.778
.866
.762
.825
.852
.808
.424
.266
.208
.165
.166
.191
.214
.196
.183
.217
.142
.335
.299
.320
.340
.853
1.045
1.425
1.497
1.691
1.479
1.530
1.521
1.192
1.064
1.099
.966
.697
.318
.401
.826
1.139
.943
.856
.843
.796
.684
.643
.663
.937
.999
1.119
1.326
1.224
1.512
1.614
1.346
1.365
1.215
.952
.241
16.8
17.4
19.2
14.2
15.0
12.8
12.3
31.3
24.1
9.6
19.8
8.4
5.4
21.5
8.5
9.0
10.2
10.0
19.7
23.2
16.2
10.7
23.2
17.2
16.5
12.2
13.8
14.1
11.7
12.7
15.1
15.8
16.0
24.4
30.9
27.3
23.7
16.8
11.4
11.9
10.8
11.4
12.8
15.0
17.0
20.8
13.2
12.9
13.8
13.6
15.1
14.2
11.7
11.1
12.1
11.7
18.7
39.8
	 *•*•*-• V* 	
29.8
19.8
24.1
16.8
17.1
15.7
12.6
64.3
71.2
16.4
42.6
17.7
10.5
59.1
20.0
16.2
23.5
19.2
30.0
38.2
39.9
37.0
35.3
22.9
17.4
12.8
14.5
14.5
11.9
12.9
17.5
16.7
16.7
71.1
83.6
43.1
32.7
22.1
13.0
12.4
11.7
13.6
15.8
16.4
20.9
41.5
14.5
14.0
14.8
15.0
15.5
14.9
12.0
11.2
12.3
11.8
20.7
66.4
25.9
26.4
27.7
27.1
26.3
25.0
22.2
20.0
19.0
15.7
14.9
15.1
13.8
13.2
12.6
11.2
11.1
11.2
12.0
14.5
17.5
19.2
23.5
25.9
28.0
28.7
28.2
28.8
28.1
26.7
24.5
23.3
22.9
22.1
21.0
20.4
19.6
20.2
21.1
20.5
20.2
19.5
19.2
20.5
24.0
26.7
26.3
27.1
28.2
28.7
29.1
28.1
27.3
25.4
22.8
21.3
20.2
18.3
-3.70
-3.09
-3.87
-2.99
-2.47
-2.04
-.47
.31
.96
1.81
1.88
.72
1.17
.89
.90
1.80
1.27
.96
.56
.09
-.41
-.70
-1.86
-.58
-3.39
-3.56
-2.73
-2.93
-2.50
-1.44
.25
.83
.82
.73
.86
.60
.82
1.29
1.09
1.02
1.24
.97
.61
-.15
-.95
-2.54
-2.69
-3.22
-3.36
-3.12
-3.40
-2.83
-2.70
-1.60
-.05
.47
.94
1.42
767.
731.
631.
479.
302.
132.
13.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
4.
88.
258.
397.
575.
693.
710.
757.
738.
625.
476.
306.
133.
12.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
105.
281.
461.
618.
727 .
793.
799.
747.
648.
492.
320.
139.
12.
0.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                       41

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S    PEG   PEG    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
260
260
260
260
260
260
260
260
260
260
260
260
260
260
260
260
260
260
260
260
261
261
261
261
261
261
261
261
261
261
261
261
261
261
261
261
261
261
261
261
261
261
261
261
262
262
262
262
262
262
262
262
262
262
262
262
262
262
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
1.7
2.4
1.5
1.9
2.1
2.8
3.2
4.4
4.6
5.0
3.9
3.4
4.0
4.6
4.4
3.3
1.1
.9
1.2
.7
1.1
1.3
1.6
1.7
1.8
1.5
1.4
1.2
1.6
.7
1.1
1.7
2.6
2.7
3.1
2.8
2.7
1.5
1.1
.8
.8
1.4
1.3
1.4
1.3
1.0
1.5
1.4
1.5
1.6
1.4
1.3
.7
1.4
3.2
3.3
3.2
2.9
223.
315.
232.
36.
36.
97.
204.
344.
150.
63.
232.
97.
67.
237.
65.
152.
313.
219.
126.
169.
151.
132.
130.
130.
126.
131.
129.
141.
138.
231.
230.
268.
284.
299.
297.
295.
282.
326.
250.
211.
123.
150.
148.
132.
134.
151.
146.
123.
138.
145.
144.
122.
190.
268.
287.
246.
123.
204.
.313
.605
.532
.654
.876
.985
.950
1.023
1.115
1.055
.964
.995
.958
1.049
1.024
.776
.332
.279
.219
.175
.201
.200
.195
.227
.180
.174
.166
.216
.379
.309
.358
.381
.502
.629
.592
.550
.405
.362
.235
.363
.228
.219
.208
.16.9
.157
.128
.187
.178
.132
.139
.164
.229
.261
.399
.425
.718
.995
1.006
10.6
15.3
24.4
17.3
23.7
18.8
18.7
15.5
15.1
13.8
15.4
17.6
14.3
12.7
11.5
11.9
16.6
15.9
19.1
18.1
13.2
6.0
6.9
6.3
4.7
7.5
8.6
9.4
15.9
33.1
27.8
16.1
14.6
18.3
12. 9
12.8
9.0
15.7
12.3
19.6
18.9
22.0
16.7
7.4
6.5
7.0
5.8
6.1
4.7
4.8
5.3
9.9
29.4
26.5
9.2
16.3
22.2
31.0
32.9
18.4
34.7
18.5
27.3
21.3
25.4
18.5
17.7
15.9
20.1
20.2
16.4
13.3
12.0
13.4
18.7
78.4
26.3
35.1
22.9
15.2
11.8
12.7
6.0
9.4
13.1
16.7
18.9
52.2
62.2
16.9
17.0
20.2
16.5
21.8
10.1
28.4
26.2
88.0
53.3
43.9
31.4
11.5
14.8
12.6
10.2
10.4
9.0
9.3
12.4
20.0
68.4
39.3
10.0
42.0
26.0
35.1
12.9
12.4
12.3
12.8
14.3
16.9
17.8
18.1
20.4
20.8
20.4
21.2
20.1
17.3
14.8
13.8
12.5
11.1
9.1
8.3
9.8
10.0
8.8
8.1
7.0
6.2
6.4
9.5
12.1
15.1
17.7
18.1
19.0
20.1
20.3
21.1
20.9
21.2
18.1
15.2
12.8
11.9
11.0
9.7
9.4
9.0
7.3
6.6
6.9
6.3
6.6
8.9
11.9
14.2
15.2
18.0
21.1
21.3
-.14
-.24
-.19
-.43
-1.09
-2.78
-2.79
-2.55
-4.12
-4.35
-3.53
-4.15
-3.40
-1.50
.02
.33
.40
1.17
2.04
1.78
.41
.33
.91
1.27
1.94
1.98
1.35
.01
-.51
-.95
-1.71
-1.18
-1.21
-1.31
-1.05
-1.14
-.77
-1.09
-.04
1.03
2.32
2.05
1.51
1.89
1.57
1.50
1.79
1.65
1.21
1.13
.77
-.23
.03
-.84
-.96
-2.16
-4.18
-3.55
0.
0.
18.
105.
231.
563.
710.
750.
754.
695.
585.
435.
260.
77.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
30.
175.
409.
557.
661.
726.
731.
682.
576.
428.
255.
83.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
56.
187.
394.
526.
654.
709.
715.
653.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      45

-------
YEAR DAY HR   WS  WD   SDWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S   PEG  PEG    °C    °C   W/M^2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
262
262
262
262
262
262
262
262
262
262
263
263
263
263
263
263
263
263
263
263
263
263
263
263
263
263
263
263
263
263
263
263
263
263
264
264
264
264
264
264
264
264
264
264
264
264
264
264
264
264
264
264
264
264
264
264
264
264
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
3.3
4.2
4.4
3.8
2.7
2.0
1.1
.8
1.1
1.5
1.8
.9
1.5
1.6
1.4
1.4
1.4
1.0
1.4
1.4
2.7
2.7
2.6
3.0
2.9
3.1
3.2
2.8
1.9
1.5
1.4
1.4
1.6
1.6
1.4
.9
1.2
1.5
.6
1.5
1.4
.9
.7
2.2
2.6
3.3
4.0
4.1
3.4
3.4
3.4
2.8
1.8
1.1
1.3
.9
1.3
1.2
309.
151.
267.
265.
11.
12.
151.
149.
234.
167.
142.
153.
142.
128.
150.
137.
140.
145.
169.
225.
240.
131.
121.
291.
208.
240.
351.
333.
326.
281.
216.
288.
163.
135.
142.
257.
141.
162.
163.
139.
126.
151.
193.
276.
295.
125.
150.
334.
276.
315.
316.
150.
289.
298.
299.
149.
156.
138.
.838
1.096
1.025
.929
.674
.464
.299
.313
.444
.317
.323
.161
.199
.209
.151
.210
.186
.250
.295
.308
.727
.825
.811
.765
.830
.749
.693
.754
.735
.394
.385
.369
.283
.262
.206
.213
.242
.208
.146
.185
.208
.183
.225
.326
.553
.871
1.118
.926
.881
.904
.956
1.015
.474
.429
.416
.283
.290
.202
17.6
14.1
13.3
14.2
12.7
13.4
25.7
33.2
27.4
18.5
8.9
14.5
8.6
8.0
6.0
7.2
4.9
14.7
13.5
19.6
26.3
17.2
20.8
16.5
17.1
16.0
13.9
16.0
27.1
20.9
26.3
17.6
21.0
8.6
11.9
23.5
28.9
16.1
11.6
6.8
9.2
12.6
23.6
10.4
17.5
15.2
17.0
14.5
16.3
15.0
18.5
28.1
23.7
29.1
28.3
34.6
19.5
13.7
21.5
17.0
13.9
15.9
14.1
14.5
70.9
99.3
52.8
36.3
24.8
31.7
18.8
18.0
8.5
14.3
10.5
19.3
15.8
33.6
36.8
20.9
23.2
20.3
21.6
19.7
15.4
17.1
32.5
27.0
79.3
24.3
55.4
11.5
31.0
37.1
41.7
42.5
30.7
9.4
20.1
20.6
55.2
13.7
21.9
22.6
21.1
15.3
20.9
18.6
19.5
30.5
25.6
37.4
52.9
69.0
29.5
22.2
21.4
22.4
21.4
19.6
16.5
15.0
13.4
12.3
13.3
11.3
9.8
9.0
7.9
6.9
6.9
5.6
6.5
9.1
11.3
14.9
19.1
21.6
22.8
23.3
24.6
24.5
23.2
20.4
18.2
17.1
15.5
15.4
12.7
10.8
10.8
11.3
9.9
9.1
8.9
7.6
8.4
11.2
13.6
16.2
19.4
23.4
24.6
24.0
25.6
25.5
24.6
22.8
20.0
18.4
17.2
15.3
13.9
12.1
-2.78
-3.71
-2.74
-1.62
.10
.52
1.10
1.52
.37
.43
.62
1.10
.96
1.08
1.00
1.30
.66
-.06
-.16
-.96
-2.88
-4.41
-4.30
-3.59
-4.32
-3.93
-2.87
-.96
.05
.21
.86
.38
.89
1.71
.94
.88
1.29
.63
1.25
1. 11
.91
.08
.05
-.72
-1.05
-3.84
-3.68
-2.10
-2.78
-2.87
-2.16
-1.30
.10
.37
.50
1.26
.98
1.84
551.
407.
249.
78.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
57.
208.
376.
523.
645.
704.
706.
655.
546.
397.
229.
69.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
57.
203.
330.
519.
637.
702.
709.
655.
543.
394.
226.
65.
1.
0.
0.
0.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      46

-------
YEAR DAY HR   WS  WD    SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S  PEG     M/S   DEC?  PEG    °C    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
265
265
265
265
265
265
265
265
265
265
265
265
265
265
265
265
265
265
265
265
265
265
265
265
266
266
266
266
266
266
266
266
266
266
266
266
266
266
266
266
266
266
266
266
266
266
266
266
267
267
267
267
267
267
267
267
267
267
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
1.0
1.5
1.1
1.8
1.5
1.5
1.2
1.1
.8
1.4
2.7
2.8
2.9
3.3
3.1
2.9
2.5
2.8
3.2
1.7
1.4
.9
1.1
.6
.8
.8
1.0
1.4
.9
.7
1.0
1.4
.8
2.2
3.1
2.6
2.6
2.9
3.0
3.1
2.7
1.6
1.6
1.8
1.1
.6
.9
.8
1.3
.9
.7
.8
.9
1.4
1.6
.9
.9
1.5
160.
132.
130.
132.
129.
139.
134.
144.
205.
250.
282.
285.
278.
281.
284.
284.
291.
279.
299.
285.
290.
134.
145.
196.
153.
157.
144.
141.
173.
154.
146.
144.
243.
280.
281.
269.
286.
280.
288.
289.
321.
315.
270.
252.
206.
188.
205.
219.
149.
156.
175.
151.
148.
139.
137.
118.
186.
270.
.239
.272
.346
.346
.155
.224
.195
.222
.239
.248
.333
.360
.330
.384
.325
.351
.426
.427
.657
.458
.459
.276
.178
.158
.183
.161
.144
.217
.165
.157
.152
.254
.268
.344
.387
.715
.696
.399
.394
.438
.612
.492
.496
.374
.358
.248
.219
.207
.198
.152
.148
.159
.175
.226
.236
.165
.231
.250
21.7
11.1
27.6
8.9
8.7
9.9
8.3
12.9
25.0
10.6
7.6
7.0
6.2
6.3
5.6
6.5
9.5
7.8
9.1
24.3
25.3
37.2
14.9
22.5
15.0
19.0
6.2
8.9
10.7
12.8
8.6
11.3
21.5
10.9
6.1
22.5
18.3
10.5
6.5
6.7
12.4
24.8
32.9
18.1
23.1
35.1
24.7
26.3
10.7
10.8
14.9
12.6
7.9
6.0
5.1
12.0
14.9
10.4
24.6
22.2
54.0
20.8
16.9
20.1
14.9
27.9
55.3
21.8
9.2
9.6
7.5
9.2
8.1
7.5
10.5
9.1
13.3
37.5
35.7
72.0
22.5
70.6
43.4
30.0
11.2
17.5
29.8
32.1
15.3
13.5
39.7
17.0
6.9
34.2
27.3
12.2
10.2
10.8
29.0
30.9
43.7
38.0
61.3
63.4
73.7
80.2
19.1
19.5
48.4
32.0
13.4
12.1
7.4
24.9
38.9
18.8
12.0
10.3
10.4
9.2
8.1
8.1
8.2
11.1
13.6
16.9
18.5
20.4
23.1
24.4
25.2
26.0
26.6
24.7
23.0
21.2
20.0
17.7
16.3
14.6
13.5
12.3
11.6
11.2
11.1
9.8
9.8
12.5
14.6
17.4
19.0
23.3
25.4
24.5
25.0
25.1
25.6
24.4
21.5
21.0
18.4
16.0
15.5
13.7
11.9
11.4
10.5
10.2
9.1
8.6
9.0
11.4
14.3
17.1
1.12
1.36
.98
1.02
1.92
1.37
1.22
.17
.04
-.75
-.90
-.92
-1.20
-1.25
-.99
-.80
-.42
-.15
.25
.57
.58
1.74
1.48
1.29
1.29
1.60
1.82
1.07
.78
1.68
1.62
-.07
-.04
-.74
-.99
-2.22
-2.69
-1.14
-.92
-.91
-1.26
-.44
.31
.38
1.32
1.32
1.11
1.48
2.11
1.79
1.89
1.66
1.86
1.76
1.01
.23
-.04
-.71
0.
0.
0.
0.
0.
1.
60.
213.
372.
526.
634.
616.
718.
657.
541.
391.
222.
53.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
47.
192.
359.
507.
567.
683.
684.
631.
522.
372.
207.
54.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
51.
201.
370.
521.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      47

-------
YEAR DAY HR   WS  WD
             M/S PEG
SDWS  SDWD SDEPA  TEMP
 M/S   PEG  PEG     °C
DTDZ SOLRAD PCPN
      W/M/V2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
267
267
267
267
267
267
267
267
267
267
267
267
267
267
268
268
268
268
268
268
268
268
268
268
268
268
268
268
268
268
268
268
268
268
268
268
268
268
269
269
269
269
269
269
269
269
269
269
269
269
269
269
269
269
269
269
269
269
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
2.6
3.3
3.7
3.2
3.2
2.5
1.9
1.5
1.8
1.4
1.0
1.3
.9
.7
.5
.3
.5
.7
.7
1.2
2.3
2.8
3.0
3.4
3.0
3.7
4.0
4.3
4.7
3.9
2.6
3.3
2.6
1.7
2.0
1.8
1.5
1.2
1.5
1.0
.9
.7
.8
1.2
.8
.9
1.2
1.5
1.7
2.5
1.7
1.8
1.7
1.9
1.0
.8
1.2
1.0
281.
285.
287.
297.
258.
177.
218.
233.
307.
287.
247.
326.
257.
128.
158.
228.
250.
94.
269.
279.
236.
233.
236.
249.
247.
248.
237.
235.
227.
226.
181.
196.
194.
165.
169.
149.
123.
233.
108.
186.
192.
168.
144.
122.
190.
180.
273.
278.
286.
294.
290.
223.
264.
240.
226.
183.
109.
116.
.317
.412
.454
.522
.806
.524
.445
.403
.509
.355
.352
.327
.217
.184
.104
.170
.145
.154
.262
.305
.403
.499
.535
.582
.612
.607
.738
.933
.991
.812
.703
.819
.664
.330
.429
.270
.332
.291
.207
.236
.196
.146
.141
.197
.252
.223
.177
.237
.289
.309
.291
.332
.341
.339
.196
.164
.171
.135
7.3
8.4
6.5
10.9
13.4
14.7
16.3
17.2
18.2
17.2
36.5
19.4
11.1
18.8
16.0
40.6
27.6
14.3
32.1
16.5
9.8
9.7
9.0
9.4
11.3
10.2
11.6
11.5
12.4
13.6
17.2
12.1
13.3
13.0
11.3
7.0
10.8
17.4
9.5
16.8
14.8
17.6
10.7
11.9
22.3
21.1
8.3
12.6
10.8
6.0
9.4
16.0
10.0
9.0
10.3
13.1
7.8
8.7
8.9
11.2
7.3
18.4
18.1
42.5
35.6
24.4
24.8
24.3
57.4
29.0
66.3
38.2
40.5
66.9
65.9
44.9
80.9
35.5
12.6
12.8
10.7
11.1
15.5
14.3
15.3
17.0
15.1
18.9
19.5
13.5
24.3
16.2
23.3
13.9
42.2
99.8
21.1
44.8
44.9
63.3
21.0
20.3
83.9
69.2
13.9
21.8
16.8
12.8
16.3
32.0
14.0
13.3
17.9
32.7
15.7
12.0
19.0
21.0
21.6
23.7
27.6
27.4
26.9
24.0
21.2
19.2
17.4
16.3
15.5
13.4
12.8
12.6
12.5
11.6
12.4
12.8
13.1
13.2
13.8
14.3
15.3
15.7
16.5
16.5
16.7
16.9
16.9
16.9
16.5
16.2
16.1
15.7
14.5
14.3
13.4
13.5
12.8
12.3
12.5
12.6
12.9
13.3
14.0
14.6
15.4
15.7
16.5
16.3
16.0
15.8
15.6
15.4
14.9
14.4
-.85
-1.08
-1.09
-1.32
-3.35
-2.44
-2.40
-1.06
.19
.48
.80
.27
.49
1.82
1.92
1.33
1.21
1.53
.47
.05
-.17
-.29
-.35
-.43
-.55
-.47
-.45
-.38
-.25
-.19
-.12
-.06
.02
.10
.08
.28
.62
.16
.60
.27
.49
.72
.31
.04
.15
-.01
-.17
-.23
-.39
-.33
-.28
-.11
-.08
-.04
-.03
.09
.34
.72
627.
684.
685.
632.
522.
368.
205.
49.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
13.
50.
80.
91.
158.
144.
176.
95.
62.
42.
27.
6.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
31.
72.
138.
127.
330.
143.
103.
74.
82.
69.
46.
18.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.11
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.02
.02
.02
.01
.01
.00
.00
                                      48

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
269
269
269
269
270
270
270
270
270
270
270
270
270
270
270
270
270
270
270
270
270
270
270
270
270
270
270
270
271
271
271
271
271
271
271
271
271
271
271
271
271
271
271
271
271
271
271
271
271
271
271
271
272
272
272
272
272
272
HR
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
WS
M/S
.9
.6
.7
.9
.6
.7
1.5
.5
.3
.8
1.8
1.6
2.5
3.2
3.4
3.6
3.4
3.2
2.7
1.7
2.5
3.2
3.6
2.0
1.5
1.5
1.4
1.3
.6
1.5
.6
.7
1.4
.8
.7
1.4
2.2
2.6
2.7
3.2
2.8
2.7
3.2
3.2
2.8
2.4
1.6
.7
.7
1.3
.7
1.1
1.2
1.3
.8
1.2
1.0
1.5
WD
DEC
92.
190.
196.
133.
112.
151.
134.
96.
172.
286.
295.
178.
40.
35.
99.
291.
348.
240.
187.
24.
207.
209.
36.
25.
46.
16.
133.
291.
170.
135.
149.
161.
141.
144.
166.
180.
47.
76.
180.
208.
211.
72.
240.
176.
269.
295.
162.
204.
235.
154.
186.
135.
127.
149.
191.
178.
100.
125.
SOWS
M/S
.168
.136
.132
.202
.132
.174
.288
.192
.163
.198
.349
.475
.760
1.064
.897
.879
.839
.833
.727
.628
.629
.634
.723
.580
.381
.474
.351
.263
.232
.205
.187
.183
.313
.240
.170
.515
.749
.762
.634
.729
.695
.663
.741
.749
.690
.627
.417
.329
.253
.242
.273
.159
.139
.232
.204
.252
.161
.279
SDWD
DEC
9.4
12.4
9.8
12.0
12.1
15.5
12.8
18.6
19.3
16.3
10.0
17.1
17.2
18.1
16.2
14.5
14.3
17.8
18.4
22.0
13.7
11.8
10.8
15.0
15.3
18.1
15.2
12.4
29.7
8.4
24.7
31.7
17.5
24.0
23.7
20.2
19.6
17.9
15.8
14.3
15.1
15.0
15.4
13.5
13.9
16.0
19.6
41.6
23.8
14.5
29.4
16.4
8.2
9.3
12.6
16.4
11.2
8.8
SDEPA
DEC
35.8
70.2
28.8
33.8
30.3
40.4
21.0
43.8
51.8
27.6
21.8
32.9
18.6
21.7
21.3
17.5
16.5
24.0
23.6
25.0
16.8
14.1
11.8
16.6
44.8
20.5
25.0
24.2
98.9
15.7
37.0
50.1
21.9
29.7
45.1
26.2
24.2
24.2
19.9
16.9
28.7
18.5
18.3
17.0
14.9
16.8
28.0
91.6
65.9
45.4
49.2
22.2
15.5
18.4
64.0
91.1
48.7
37.8
TEMP
°C
13.2
13.2
12.4
12.2
12.5
12.9
12.7
12.8
13.1
13.1
13.4
14.3
15.9
17.5
18.7
18.5
18.7
21.4
22.7
22.8
21.4
18.4
16.2
15.2
14.5
13.9
13.3
12.5
11.5
10.0
10.1
11.3
11.9
12.4
12.9
14.4
15.0
16.2
18.0
19.6
20.8
23.6
23.3
23.4
23.1
20.2
17.6
16.3
15.2
14.0
13.4
12.0
11.5
11.6
11.0
11.1
9.5
9.5
DTDZ
°C
1.27
.48
.21
-.20
-.12
-.13
-.18
-.17
-.14
-.05
-.14
-.03
-.44
-1.04
-1.77
-1.27
-1.43
-3.44
-4.32
-4.15
-2.92
-1.03
.10
.67
.83
.75
.75
.91
1.20
.32
.34
-.12
-.04
-.09
-.03
-.31
-.81
-1.65
-2.64
-3.45
-3.68
-4.87
-3.80
-3.28
-2.76
-1.03
.63
.77
1.14
1.20
.86
1.25
1.31
.63
.94
.79
.97
1.02
SOLRAD
W/MA2
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
"7.
65.
202.
262.
368.
318.
338.
590.
480.
339.
169.
35.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
8.
50.
111.
252.
521.
655.
653.
596.
475.
336.
171.
34.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
49

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
272
272
272
272
272
272
272
272
272
272
272
272
272
272
272
272
272
272
273
273
273
273
273
273
273
273
273
273
273
273
273
273
273
273
273
273
273
273
273
273
273
273
274
274
274
274
274
274
274
274
274
274
274
274
274
274
274
274
HR
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
WS
M/S
1.0
1.3
1.4
1.1
1.6
2.4
2.8
3.7
3.2
5.0
4.1
3.0
2.9
3.5
2.3
1.7
2.0
1.9
2.4
.9
.7
.5
1.0
1.3
1.6
2.3
3.6
3.5
4.5
4.6
4.3
3.9
4.4
5.7
5.4
4.1
3.5
4.5
4.7
3.8
3.0
3.2
2.7
2.4
2.2
1.9
1.6
1.6
1.2
1.2
1.4
1.1
1.8
1.3
2.7
3.6
4.0
4.2
WD
DEC
133.
147.
166.
224.
278.
286.
300.
296.
231.
246.
264.
261.
260.
259.
258.
195.
154.
237.
248.
263.
300.
302.
220.
232.
251.
260.
260.
253.
254.
260.
257.
252.
248.
243.
241.
219.
206.
223.
211.
198.
176.
176.
175.
176.
176.
178.
162.
144.
121.
145.
155.
180.
288.
291.
291.
312.
236.
346.
SOWS
M/S
.245
.276
.310
.306
.271
.356
.473
.616
.696
.982
.684
.538
.492
.598
.417
.318
.367
.425
.513
.259
.177
.147
.196
.234
.295
.374
.528
.647
.866
.800
.888
.864
.921
.997
.962
.900
.810
.858
.925
.937
.759
.757
.708
.547
.459
.490
.289
.262
.255
.235
.317
.434
.307
.267
.536
.684
1.086
1.082
SDWD
DEC
20.5
11.2
13.8
16.0
12.6
9.0
9.6
9.6
12.3
10.9
10.0
10.0
8.7
10.0
9.5
12.9
9.4
14.8
10.6
20.0
19.0
21.7
13.1
10.3
9.5
10.1
9.0
10.0
9.5
10.8
12.8
14.8
13.0
11.2
9.5
10.8
11.7
10.2
10.1
11.9
13.6
11.9
12.5
12.3
12.8
12.1
11.1
9.5
12.7
10.6
12.2
32.2
11.8
13.8
17.3
14.5
16.6
15.4
SDEPA
DEC
49.4
14.3
24.7
39.8
15.8
10.7
20.4
18.3
15.0
25.9
13.0
11.3
11.0
11.7
11.5
53.4
14.3
36.1
12.2
29.9
31.9
30.5
35.2
34.8
14.9
18.1
9.4
11.5
11.6
12.8
14.1
18.7
16.3
12.5
11.1
15.6
16.1
13.1
14.0
14.0
15.4
12.4
12.8
13.0
14.5
15.6
21.8
12.5
27.8
13.8
15.6
62.5
16.3
25.8
23.5
27.3
20.3
16.8
TEMP
°C
10.1
11.0
11.5
13.1
15.1
17.9
20.1
20.5
22.1
20.5
17.6
16.6
16.4
16.1
16.1
16.1
16.1
16.5
16.0
15.7
15.4
15.2
15.1
15.0
15.2
15.0
15.1
15.3
16.1
17.5
18.0
18.6
18.6
18.6
17.9
16.9
15.8
15.4
14.5
13.7
13.6
13.8
13.9
13.9
13.8
13.6
13.2
12.8
12.5
12.8
13.5
15.2
14.9
15.2
17.0
18.7
20.2
19.3
DTDZ
°C
-.03
-.23
-.32
-.79
-.74
-.74
-.85
-.77
-.49
-.33
-.26
-.05
-.07
-.10
-.09
-.04-
.06
-.02
-.10
-.07
-.06
-.07
-.10
-.03
-.03
-.08
-.05
-.14
-.36
-1.05
-1.09
-1.33
-1.03
-.86
-.50
-.12
-.01
-.09
-.15
-.14
-.09
-.09
-.10
-.07
-.03
-.01
-.04
.08
.20
.02
-.32
-.71
-.45
-.43
-1.05
-1.77
-3.16
-2.52
SOLRAD
W/M"2
13.
81.
198.
382.
371.
560.
412.
411.
240.
119.
39.
9.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
5.
14.
38.
75.
308.
637.
617.
651.
454.
371.
181.
31.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
16.
45.
152.
357.
212.
153.
679.
603.
483.
353.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
50

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S    PEG  PEG    °C    °C   W/M"2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
274
274
274
274
274
274
274
274
275
275
275
275
275
275
275
275
275
275
275
275
275
275
275
275
275
275
275
275
275
275
275
275
276
276
276
276
276
276
276
276
276
276
276
276
276
276
276
276
276
276
276
276
276
276
276
276
277
277
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
5.7
4.4
3.6
3.6
3.1
2.8
3.5
3.4
4.2
2.1
2.5
2.5
1.9
1.2
1.1
1.4
2.0
2.5
3.4
3.7
3.3
5.4
5.2
4.0
3.2
3.5
3.4
2.7
1.6
1.6
1.8
1.3
.8
1.9
1.6
1.7
1.2
1.2
1.5
1.4
1.0
.8
.9
1.6
2.4
2.3
2.0
2.1
1.7
1.0
.4
.9
.9
1.0
1.8
1.0
1.5
1.3
181.
356.
182.
20.
25.
28.
36.
38.
24.
58.
25.
67.
68.
184.
130.
168.
89.
72.
94.
237.
152.
324.
322.
342.
292.
322.
124.
30.
125.
132.
145.
132.
158.
135.
142.
137.
149.
149.
147.
118.
122.
166.
243.
250.
282.
293.
294.
293.
317.
254.
268.
154.
141.
198.
149.
142.
158.
127.
1.271
1.094
.960
.974
.965
.815
.950
1.020
1.198
1.006
1.027
1.005
.734
.325
.316
.667
.828
.927
1.068
1.085
1.068
1.344
1.266
1.046
.808
.868
.811
.733
.512
.280
.219
.316
.172
.223
.185
.198
.112
.154
.153
.188
.226
.319
.232
.272
.309
.415
.467
.408
.326
.280
.132
.401
.184
.318
.286
.165
.181
.215
13.1
14.6
13.7
14.2
15.3
14.8
12.7
15.5
15.1
30.1
21.5
28.7
22.5
32.2
25.7
43.2
36.0
34.2
21.2
17.0
19.8
14.1
13.7
14.3
14.3
12.6
12.5
14.4
22.5
9.5
6.1
19.0
17.6
5.0
6.7
4.8
5.6
5.8
5.5
7.5
17.8
34.5
17.5
8.1
8.3
15.2
18.5
13.2
12.9
15.6
22.3
38.7
13.4
17.1
9.7
13.7
8.0
9.6
13.5
14.9
15.4
16.5
16.6
15.2
14.1
18.9
17.2
33.6
25.0
36.6
48.9
55.4
33.8
80.1
77.8
40.4
23.2
19.0
21.6
14.7
16.5
15.6
16.1
14.5
15.0
15.1
82.1
17.6
8.4
29.3
36.1
7.4
11.5
6.4
8.9
12.2
10.5
11.5
23.7
61.2
21.3
17.9
8.9
21.9
25.6
19.2
29.8
29.5
58.6
91.6
34.1
43.4
19.8
27.3
9.3
18.0
18.2
15.7
14.5
13.9
13.6
13.6
13.3
13.2
13.3
12.3
12.0
11.6
10.8
10.1
9.3
11.5
13.6
16.3
17.4
18.7
20.4
20.5
20.8
20.5
20.2
16.9
15.0
14.1
13.6
9.5
8.4
7.3
6.6
5.0
5.1
4.0
4.5
3.7
3.3
5.3
8.7
12.9
15.0
16.8
17.2
18.9
20.0
20.0
20.5
18.6
13.8
12.2
10.7
11.1
9.0
6.8
7.9
5.3
-2.05
-.50
.15
.36
.44
.43
.57
.44
.21
.47
.45
.46
.53
.71
1.01
.18
-.50
-2.16
-2.38
-2.82
-3.38
-3.11
-2.85
-2.32
-2.59
-.70
.48
1.16
1.15
1.70
1.66
1.55
1.74
1.71
1.12
1.51
1.09
1.41
1.31
.04
-.37
-1.07
-1.24
-1.23
-.96
-1.16
-1.17
-.84
-1.21
-.12
1.66
1.82
2.69
2.21
1.08
3.35
1.19
2.25
165.
20.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
33.
181.
352.
501.
608.
661.
653.
605.
496.
349.
175.
25.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
31.
162.
342.
492.
598.
648.
641.
574.
467.
331.
162.
21.
0.
0.
0.
0.
0.
0.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      51

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
277
277
277
277
277
277
277
277
277
277
277
277
277
277
277
277
277
277
277
277
277
277
278
278
278
278
278
278
278
278
278
278
278
278
278
278
278
278
278
278
278
278
278
278
278
278
279
279
279
279
279
279
279
279
279
279
279
279
HR
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
WS
M/S
1.7
1.8
1.7
1.8
1.8
2.4
1.8
1.2
1.1
1.2
1.2
1.2
2.7
1.7
.6
1.0
1.4
.6
1.1
.9
.6
.9
1.1
1.4
.8
1.4
.7
.9
1.6
1.2
1.0
1.6
2.1
2.4
3.0
3.8
2.1
2.4
2.3
1.9
1.8
1.3
.7
1.8
1.8
1.2
.9
.7
1.0
1.3
1.1
1.6
1.6
.9
.8
1.0
1.8
1.9
WD
DEC
143.
128.
120.
148.
133.
154.
154.
148.
131.
134.
149.
266.
285.
287.
220.
265.
300.
157.
122.
152.
148.
167.
143.
146.
142.
156.
198.
125.
146.
174.
193.
269.
286.
289.
294.
294.
337.
94.
94.
287.
298.
209.
221.
305.
310.
283.
233.
95.
311.
231.
197.
66.
68.
126.
208.
261.
294.
331.
SOWS
M/S
.246
.192
.183
.289
.293
.407
.378
.330
.399
.386
.437
.427
.302
.198
.161
.175
.234
.174
.134
.167
.154
.170
.132
.204
.138
.258
.170
.157
.242
.295
.275
.267
.298
.386
.353
.488
.486
.491
.550
.544
.595
.542
.335
.483
.539
.525
.404
.182
.342
.572
.516
.359
.463
.214
.203
.258
.404
.466
SDWD SDEPA
DEC DEC
8.1
7.7
8.7
10.5
7.8
8.8
11.6
14.9
24.8
28.9
21.7
35.1
5.2
4.9
21.1
10.8
7.5
17.1
5.3
19.6
15.6
16.3
24.9
7.7
11.8
9.5
19.8
9.4
8.0
15.9
28.0
10.4
10.6
10.2
7.8
7.3
16.1
15.4
14.1
18.1
20.7
30.6
36.7
17.7
22.5
36.1
34.2
28.8
21.4
24.3
42.4
12.1
20.1
19.3
16.0
16.0
19.5
17.6
13.6
22.4
16.1
13.7
14.5
13.4
16.0
17.2
27.7
35.7
24.9
50.3
6.8
6.4
73.4
23.7
11.9
82.2
16.5
35.4
74.1
33.5
33.3
11.7
27.7
20.8
86.9
32.1
20.3
56.2
39.5
24.1
16.9
16.9
9.2
9.8
22.9
18.0
16.9
22.1
33.1
55.1
58.5
22.0
24.8
48.2
86.7
55.2
32.0
44.8
63.7
18.9
29.3
27.9
42.8
63.6
22.0
27.0
TEMP
°C
5.6
4.3
4.6
5.3
7.1
8.2
9.1
10.4
11.4
12.7
14.0
14.9
14.1
14.4
14.6
14.3
13.2
12.8
12.4
11.7
11.1
10.7
9.7
9.5
9.1
8.9
8.1
8.4
8.7
9.7
12.0
13.7
15.1
16.7
17.0
16.9
18.5
18.5
18.0
16.6
15.2
14.7
14.0
13.7
13.1
12.6
11.9
10.6
11.0
11.8
11.9
11.7
11.5
11.8
12.0
12.9
13.1
14.0
DTDZ SOLRAD
°C W/M^2
1.24
1.70
2.15
.64
.35
-.13
-.31
-.54
-.83
-.95
-.89
-.68
-.44
-.30
-.13
-.10
-.09
.24
.53
.71
.86
.38
.64
.09
.23
.28
.89
.71
.13
-.19
.04
-.54
-.62
-.75
-.67
-.59
-1.20
-1.43
-1.38
-.33
.01
.08
.35
.15
.05
.19
.41
1.10
.77
.11
-.13
-.22
-.25
-.32
-.29
-.68
-.49
-.98
0.
0.
0.
0.
11.
29.
89.
128.
209.
216.
309.
238.
105.
46.
24.
5.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
39.
131.
323.
284.
382.
517.
306.
277 .
224.
154.
97.
18.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
4.
24.
75.
114.
181.
202.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.02
.01
.00
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
52

-------
YEAR DAY HR   WS  WD   SDWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S    PEG   PEG     °C    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
279
279
279
279
279
279
279
279
279
279
279
279
280
280
280
280
280
280
280
280
280
280
280
280
280
280
280
280
280
280
280
280
280
280
280
280
281
281
281
281
281
281
281
281
281
281
281
281
281
281
281
281
281
281
281
281
281
281
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
1.8
2.2
2.6
2.2
2.2
1.8
1.2
.9
1.0
.5
.6
1.2
1.1
1.0
1.3
1.7
.8
1.5
2.2
1.8
1.2
.7
1.5
1.3
1.2
1.8
1.7
1.5
2.3
1.8
1.3
1.0
.9
.6
.6
.8
.9
.4
.7
1.7
.8
.7
1.4
.4
.5
.7
1.2
2.1
3.2
2.7
2.6
2.6
2.0
1.6
1.0
1.2
.7
.7
175.
297.
281.
278.
299.
264.
258.
265.
160.
207.
157.
155.
130.
149.
137.
132.
122.
151.
146.
146.
120.
113.
242.
246.
261.
318.
304.
281.
290.
303.
288.
278.
291.
157.
211.
134.
161.
230.
175.
138.
184.
165.
142.
105.
197.
254.
268.
290.
285.
281.
280.
286.
285.
299.
291.
301.
194.
190,
.539
.506
.322
.304
.346
.339
.298
.241
.188
.173
.139
.196
.168
.147
.179
.254
.166
.242
.294
.347
.227
.218
.358
.273
.292
.383
.320
.249
.338
.316
.223
.138
.171
.191
.152
.127
.187
.120
.157
.291
.154
.160
.232
.144
.198
.257
.247
.356
.419
.365
.320
.300
.265
.206
.247
.258
.204
.153
22.8
18.8
7.5
8.4
10.5
11.5
14.2
16.2
12.2
14.8
26.2
14.5
6.6
7.7
8.8
8.0
12.2
7.7
6.5
8.2
12.2
30.8
24.2
24.5
23.4
13.0
10.5
10.6
7.3
9.1
9.9
8.4
9.5
23.9
28.7
12.7
10.2
16.2
13.6
6.7
9.5
14.2
6.8
24.7
29.7
33.8
16.9
11.3
8.0
7.6
6.0
5.6
5.5
5.9
18.4
9.3
16.4
18.4
31.6
33.0
11.1
13.0
13.9
23.1
24.2
38.0
48.3
91.9
78.0
29.4
14.0
21.4
26.3
23.1
29.6
8.9
9.5
9.1
21.4
35.9
39.3
50.3
54.3
25.8
17.1
18.6
15.0
14.3
22.5
26.8
29.6
75.8
80.6
78.8
19.9
64.0
53.4
10.5
35.4
32.9
8.9
35.8
89.0
68.8
28.0
21.7
9.1
10.3
6.8
6.1
6.5
6.6
40.3
21.0
93.7
75.8
14.8
15.4
15.8
17.1
17.1
15.1
12.9
12.1
11.1
10.5
9.5
9.2
8.7
9.1
9.2
9.6
10.1
10.4
10.5
10.9
11.7
12.4
13.3
14.2
15.3
15.7
15.6
15.6
15.1
14.6
14.1
14.1
13.7
12.3
12.3
11.4
10.9
10.4
10.4
10.4
10.9
11.1
10.9
11.3
11.8
12.4
13.3
14.4
16.5
17.7
17.9
17.5
16.8
15.4
13.9
13.1
12.1
10.7
-1.44
-1.15
-.84
-.87
-.50
-.44
.36
.78
1.19
1.20
1.62
1.23
1.30
.76
.25
-.01
-.19
-.10
-.12
-.21
-.53
-.53
-.51
-.62
-.95
-.91
-.43
-.30
-.33
-.13
-.10
-.01
.17
1.26
.75
1.18
.65
.67
.21
-.14
-.10
-.14
-.15
-.30
-.32
-.29
-.46
-.81
-.89
-.93
-1.11
-.73
-.59
.20
.39
.31
1.08
1.72
247.
409.
390.
321.
162.
13.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
7.
36.
85.
94.
122.
156.
232.
260.
127.
79.
44.
10.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
5.
36.
72.
118.
224.
536.
568.
520.
417.
286.
119.
10.
0.
0.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      53

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S   PEG  PEG    °C    °C   W/M"2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
286
286
286
286
286
286
287
287
287
287
287
287
287
287
287
287
287
287
287
287
287
287
287
287
287
287
287
287
287
287
288
288
288
288
288
288
288
288
288
288
288
288
288
288
288
288
288
288
288
288
288
288
288
288
289
289
289
289
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
1.6
.9
1.2
2.1
2.0
1.4
1.0
1.4
1.6
1.2
1.4
1.9
.7
.8
1.1
1.0
1.0
1.9
3.9
3.5
3.8
4.1
3.7
3.9
2.6
2.1
3.5
2.3
1.6
1.1
1.7
1.7
1.9
1.7
1.5
1.9
1.8
1.8
1.0
1.0
1.5
2.1
2.5
2.5
2.8
2.8
2.1
1.5
1.3
.7
1.2
1.1
2.0
1.7
.8
2.1
1.5
1.3
212.
148.
168.
144.
150.
124.
107.
161.
135.
138.
127.
144.
137.
182.
138.
193.
250.
150.
44.
181.
322.
344.
324.
65.
14.
25.
41.
85.
81.
128.
144.
146.
144.
138.
135.
140.
137.
136.
138.
189.
289.
168.
69.
181.
287.
289.
147.
335.
276.
292.
204.
138.
162.
138.
131.
140.
121.
147.
.552
.353
.239
.258
.259
.197
.132
.215
.280
.201
.221
.224
.200
.155
.184
.222
.266
.648
1.099
1.110
1.041
.985
.886
.910
.708
.584
1.068
.814
.384
.209
.183
.146
.180
.212
.182
.225
.397
.354
.239
.260
.457
.577
.630
.704
.751
.712
.571
.512
.239
.229
.265
.272
.414
.261
.178
.278
.216
.177
27.0
32.4
16.8
8.4
7.8
7.7
9.3
8.7
12.3
17.4
12.9
7.9
21.9
13.9
11.9
16.1
26.8
21.1
17.5
16.9
14.8
14.0
13.2
11.5
12.9
14.5
13.8
18.9
13.1
29.3
5.9
5.0
4.8
5.5
8.3
6.1
11.0
9.9
16.8
21.6
21.4
21.8
14.5
17.5
17.1
16.1
17.8
18.6
10.2
31.5
26.1
22.8
22.3
7.3
18.3
6.7
10.7
6.8
31.9
43.4
18.6
17.9
20.0
21.0
18.4
20.1
31.3
31.2
22.0
23.0
51.9
17.9
27.8
29.8
32.3
39.2
21.2
20.1
17.7
14.7
14.2
12.9
13.2
15.9
20.1
38.1
23.8
67.6
12.9
9.6
10.3
7.9
11.7
9.8
19.1
11.7
23.5
39.1
50.0
34.4
17.9
21.4
22.4
21.9
29.3
23.8
27.9
44.0
83.9
32.7
53.8
17.9
61.5
10.7
16.9
13.1
13.8
12.1
11.3
9.7
9.7
8.4
9.3
10.1
8.7
8.0
7.2
7.0
5.8
7.2
8.6
10.1
11.9
14.4
16.0
16.8
16.1
15.6
14.9
12.1
10.7
9.6
9.7
9.4
7.6
5.9
4.4
3.5
2.8
1.8
1.4
1.3
2.0
2.3
4.9
8.4
11.3
14.1
15.4
15.7
15.7
15.8
14.5
11.7
9.1
9.1
7.7
5.5
5.3
4.9
4.5
3.7
2.9
2.9
.33
.93
.57
.94
.64
1.36
.96
.05
.58
.71
.70
.63
1.10
.17
-.41
-.50
-.90
-1.87
-2.96
-3.18
-2.37
-2.02
-1.88
-.01
.73
1.01
.81
.73
1.19
1.31
.94
.82
.88
1.05
1.09
.57
-.31
-.19
-.48
-.98
-1.39
-2.63
-3.14
-2.97
-2.63
-2.73
-1.95
-.08
1.12
.93
1.09
1.93
.98
.52
1.12
.58
.74
.85
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
7.
62.
97.
275.
326.
391.
539.
484.
356.
262.
103.
5.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
9.
99.
272.
433.
544.
510.
413.
378.
485.
274.
93.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      56

-------
YEAR DAY HR   WS  WD   SDWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S    PEG   PEG     °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
289
289
289
289
289
289
289
289
289
289
289
289
289
289
289
289
289
289
289
289
290
290
290
290
290
290
290
290
290
290
290
290
290
290
290
290
290
290
290
290
290
290
290
290
291
291
291
291
291
291
291
291
291
291
291
291
291
291
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
1.7
1.5
1.5
1.7
1.6
1.4
1.0
2.3
2.7
2.9
2.8
1.7
1.8
1.9
1.8
1.0
1.4
.8
.8
.9
.8
1.3
1.7
1.0
1.4
1.1
1.4
1.1
.7
.6
2.0
2.4
2.7
3.4
3.3
2.9
2.4
1.5
.6
1.0
1.1
1.8
1.1
1.0
1.1
1.5
1.6
1.8
2.4
1.5
1.4
1.3
1.8
3.8
3.5
2.5
1.8
2.9
136.
145.
142.
131.
139.
159.
240.
281.
279.
282.
282.
276.
301.
299.
303.
193.
139.
178.
159.
172.
126.
137.
137.
163.
159.
162.
135.
142.
161.
166.
284.
287.
292.
291.
292.
289.
287.
304.
227.
137.
140.
131.
178.
170.
150.
138.
114.
126.
128.
131.
160.
261.
145.
127.
127.
132.
142.
179.
.206
.147
.140
.214
.256
.295
.257
.344
.337
.358
.306
.233
.242
.231
.298
.258
.182
.143
.144
.152
.150
.152
.237
.180
.277
.184
.219
.236
.209
.233
.290
.296
.409
.441
.450
.346
.252
.270
.239
.262
.195
.221
.243
.319
.254
.304
.483
.384
.455
.301
.462
.431
.467
.517
.566
.528
.456
.695
7.2
5.7
3.9
6.0
10.4
15.0
16.8
9.9
6.9
6.2
5.7
8.3
7.2
4.5
9.3
16.9
10.4
13.1
21.5
11.7
10.0
7.3
6.9
14.5
13.8
10.6
6.4
13.9
21.0
28.1
9.0
7.7
7.2
7.0
7.2
5.6
4.9
12.4
25.9
18.3
8.7
6.7
20.9
27.0
37.5
12.6
18. 5x
10.2
9.6
19.3
35.6
31.0
17.1
6.9
7.9
9.0
15.4
12.4
16.4
9.5
7.9
8.9
18.0
24.4
25.1
12.8
7.1
6.5
7.0
9.5
16.0
8.2
16.8
77.2
20.9
43.5
53.8
33.2
17.1
17.5
11.8
33.1
38.4
47.1
12.0
28.5
47.2
76.7
19.4
10.1
14.4
9.2
10.3
8.5
5.7
17.9
65.3
63.7
21.0
14.2
45.7
85.1
48.1
19.5
26.7
16.7
17.8
39.8
84.1
50.2
27.5
9.2
8.3
10.3
21.8
12.7
2.3
1.7
1.1
2.5
4.3
7.0
10.3
11.4
13.2
14.3
14.7
16.1
13.9
12.6
12.0
10.1
8.9
9.5
9.0
9.1
8.8
7.9
7.3
6.9
6.3
5.2
5.1
6.6
10.0
14.7
15.6
17.1
18.4
20.3
21.3
21.3
18.8
15.8
12.9
12.1
11.3
10.3
10.0
9.1
8.2
7.6
8.2
8.7
9.7
11.3
12.4
12.4
11.6
11.1
11.5
12.6
14.6
15.7
.75
1.15
1.34
.19
-.48
-.68
-1.29
-.84
-.83
-.82
-.74
-.92
-.05
.23
.23
1.27
1.21
.19
.64
.36
.41
1.00
.68
1.09
.86
1.73
1.18
.57
-.21
-1.28
-.75
-.83
-.89
-.79
-.74
-.50
.05
.37
2.43
2.22
1.82
2.38
1.56
1.81
1.72
1.48
.72
.19
.29
.37
.77
.44
.15
-.02
-.23
-.53
-.66
-.29
0.
0.
9.
112.
167.
353.
505.
533.
511.
416.
319.
271.
44.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
6.
106.
253.
387.
489.
533.
523.
463.
367.
225.
79.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
9.
19.
32.
96.
190.
309.
199.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.02
.01
.02
.02
.01
.00
.00
                                      57

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
298
298
298
298
299
299
299
299
299
299
299
299
299
299
299
299
299
299
299
299
299
299
299
299
299
299
299
299
300
300
300
300
300
300
300
300
300
300
300
300
300
300
300
300
300
300
300
300
300
300
300
300
301
301
301
301
301
301
HR
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
WS
M/fl
2.0
3.1
3.3
3.0
3.1
2.6
2.7
3.5
4.3
4.6
3.7
1.9
1.3
2.1
3.4
3.0
3.5
3.3
3.9
3.1
2.8
2.3
2.8
1.9
1.9
1.7
1.7
1.0
.9
.8
.6
1.1
1.4
1.1
.8
1.4
1.2
1.8
2.6
2.6
2.9
2.8
2.7
2.2
1.7
1.2
.5
1.0
1.1
1.2
1.2
.9
1.5
1.6
1.3
1.5
1.4
1.2
WD
DEC
137.
144.
134.
138.
137.
134.
151.
161.
157.
135.
138.
134.
178.
214.
185.
164.
138.
141.
170.
170.
176.
188.
178.
128.
132.
110.
124.
101.
208.
226.
122.
156.
174.
133.
147.
204.
176.
233.
233.
264.
317.
297.
206.
70.
265.
93.
100.
129.
135.
148.
129.
161.
146.
128.
153.
138.
138.
148.
SOWS
M/S
.279
.569
.573
.493
.572
.386
.619
.845
.838
.961
.841
.477
.419
.497
.835
.636
.638
.673
.826
.657
.640
.560
.715
.437
.324
.322
.220
.212
.307
.323
.202
.297
.333
.283
.227
.393
.442
.425
.531
.532
.567
.528
.668
.639
.472
.305
.174
.203
.132
.147
.144
.134
.193
.245
.270
.206
.210
.233
SDWD
DEC
6.9
8.3
7.8
7.8
8.4
7.6
10.7
12.1
10.4
9.6
10.2
15.7
20.7
13.7
14.9
13.2
9.4
10.5
12.7
12.2
11.7
11.8
14.6
17.5
9.3
9.2
7.5
30.7
33.8
28.6
27.5
16.0
12.8
15.6
24.1
22.7
27.3
17.9
13.5
14.4
12.7
13.1
16.7
17.0
16.1
14.1
32.4
10.9
8.5
6.3
8.9
8.7
5.9
9.8
9.9
8.9
11.2
21.4
SDEPA
DEC
7.6
13.4
8.2
9.3
8.9
8.4
16.8
12.8
11.7
12.7
13.2
18.0
33.7
37.7
25.7
27.1
13.3
15.1
17.3
14.2
13.1
15.9
16.9
29.1
14.7
20.0
11.0
61.5
78.5
62.9
53.4
36.3
17.8
27.2
36.1
58.5
43.1
28.3
16.4
31.3
17.1
23.4
21.2
19.7
23.7
30.5
64.8
24.5
20.5
12.6
20.1
20.6
11.3
15.9
29.2
12.8
18.5
37.4
TEMP
°C
11.0
11.2
11.3
10.8
11.0
10.6
11.1
10.5
9.9
9.5
9.7
9.9
10.5
10.4
9.8
9.1
9.1
9.9
11.4
11.5
11.3
10.1
9.3
7.7
6.7
6.0
5.8
5.4
5.7
6.4
6.1
6.8
7.0
6.7
6.8
7.3
8.6
9.2
9.9
10.3
10.5
11.7
13.9
12.8
11.3
9.0
8.6
8.6
7.7
7.0
6.4
6.2
5.5
5.2
4.9
4.8
4.8
5.0
DTDZ
°C
.60
.44
.27
.55
.37
.56
.34
.16
.25
.33
.34
.38
.14
-.06
.00
.01
-.01
-.29
-.41
-.23
-.10
.09
.11
.73
1.03
1.76
1.79
1.62
1.16
.48
.64
.31
.05
.23
.23
.08
-.49
-.41
-.44
-.60
-.57
-1.21
-2.91
-1.89
-.67
.85
.78
.51
.66
.75
.86
.49
.54
.19
.25
.13
-.05
-.12
SOLRAD
W/MA2
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
6.
26.
64.
25.
50.
64.
222.
256.
133.
49.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
34.
208.
167.
228.
262.
322.
477.
332.
133.
32.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
PCPN
IN
.00
.00
.00
.01
.01
.00
.03
.08
.10
.01
.00
.00
.00
.01
.10
.05
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.02
61

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
301
301
301
301
301
301
301
301
301
301
301
301
301
301
301
301
301
301
302
302
302
302
302
302
302
302
302
302
302
302
302
302
302
302
302
302
302
302
302
302
302
302
303
303
303
303
303
303
303
303
303
303
303
303
303
303
303
303
HR
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
WS
M/S
1.4
1.4
2.3
1.1
1.7
2.4
2.6
2.7
2.7
2.9
2.6
1.4
.8
.6
.9
1.8
.9
1.5
1.5
1.8
1.0
1.7
1.7
1.6
1.9
1.9
1.7
1.1
1.8
1.6
1.3
2.3
2.4
2.3
2.3
1.1
1.2
1.4
.8
.9
1.4
1.4
1.5
1.2
2.2
1.6
.4
1.7
1.9
1.7
1.4
1.2
1.4
1.5
2.0
3.1
3.1
2.0
WD
DEC
145.
146.
143.
190.
277.
179.
99.
69.
150.
233.
350.
198.
292.
253.
120.
143.
198.
146.
151.
143.
132.
136.
134.
126.
134.
133.
136.
121.
146.
165.
237.
271.
235.
99.
320.
308.
234.
92.
236.
115.
141.
141.
141.
147.
146.
140.
200.
137.
146.
122.
136.
200.
179.
145.
135.
131.
134.
116.
SOWS
M/S
.241
.271
.416
.271
.430
.716
.688
.756
.754
.625
.677
.338
.229
.264
.424
.363
.136
.177
.177
.214
.153
.162
.259
.324
.346
.347
.306
.217
.327
.321
.361
.455
.621
.634
.662
.332
.576
.569
.364
.373
.261
.356
.225
.177
.347
.373
.150
.322
.343
.339
.249
.335
.376
.477
.461
.547
.543
.390
SDWD
DEC
9.1
11.2
8.1
19.2
17.2
15.7
16.2
19.0
16.0
13.2
13.1
24.9
22.6
37.9
43.1
11.1
20.8
6.0
5.1
4.9
7.8
4.0
7.1
9.1
9.7
9.0
10.6
15.0
10.0
11.3
18.0
22.2
16.6
17.1
15.8
21.3
28.3
29.9
45.8
32.1
14.3
18.4
6.3
8.1
6.8
9.5
22.5
8.1
8.2
9.8
14.8
19.0
17.5
22.7
13.8
11.5
10.2
10.9
SDEPA
DEC
12.4
18.7
9.9
51.8
34.8
21.4
24.1
21.3
19.3
18.7
13.5
46.2
33.0
65.2
89.7
14.4
75.7
14.0
10.5
11.8
18.1
5.7
11.9
11.6
11.9
13.0
16.1
20.5
11.5
17.0
31.9
37.1
25.0
23.7
18.2
25.1
36.6
49.6
86.3
54.8
19.7
29.8
11.3
13.1
8.3
16.2
63.0
11.9
10.5
18.5
19.8
30.2
49.8
33.2
18.0
14.1
11.5
27.0
TEMP
°C
5.1
5.1
5.7
8.1
9.6
12.8
14.3
14.4
14.4
12.9
10.8
8.8
7.6
7.8
6.9
4.5
3.4
3.0
2.5
1.6
.1
-.2
-.3
.2
.4
.6
1.7
3.6
4.6
6.3
8.8
10.1
11.2
11.5
9.8
8.3
7.6
7.0
6.9
5.9
3.8
3.3
2.4
1.3
1.7
1.9
2.6
2.8
2.9
3.8
4.5
5.1
6.3
7.3
8.3
8.8
8.1
8.2
DTDZ
°C
-.11
-.19
-.33
-.86
-1.00
-2.75
-3.67
-3.50
-3.31
-2.02
-.62
.44
1.18
.62
.64
.49
1.39
.74
.67
.54
1.55
.63
-.17
-.35
-.33
-.42
-.47
-.81
-.59
-.54
-1.06
-1.19
-2.05
-2.37
-.91
.06
.49
.59
.35
.85
.98
.58
.84
1.18
-.01
-.18
-.20
-.23
-.14
-.19
-.24
-.14
-.57
-.71
-1.11
-1.04
-.56
-.31
SOLRAD
W/M"2
0.
23.
151.
342.
417.
483.
487.
425.
316.
162.
31.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
33.
66.
117.
184.
292.
495.
403.
232.
187.
40.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
10.
49.
85.
137.
206.
298.
192.
114.
34.
PCPN
IN
.01
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
62

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
303
303
303
303
303
303
303
303
304
304
304
304
304
304
304
304
304
304
304
304
304
304
304
304
304
304
304
304
304
304
304
304
305
305
305
305
305
305
305
305
305
305
305
305
305
305
305
305
305
305
305
305
305
305
305
305
306
306
HR
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
WS
M/fl
1.7
1.6
.8
1.0
1.0
2.5
4.8
3.8
2.2
1.4
1.4
1.4
1.9
1.5
1.0
1.6
2.4
2.4
2.6
2.8
3.4
2.9
2.7
2.2
1.9
2.0
1.5
1.7
.9
1.7
.9
1.3
2.0
2.2
1.9
1.1
1.1
1.3
1.5
1.7
1.4
1.6
1.6
.8
1.7
2.1
2.4
2.0
2.0
2.2
1.2
.7
.9
1.4
1.1
1.4
1.7
1.0
WD
DEC
53.
75.
238.
81.
242.
17.
16.
26.
67.
72.
44.
35.
30.
111.
72.
36.
54.
39.
36.
214.
155.
257.
232.
289.
331.
285.
151.
40.
168.
79.
96.
175.
168.
128.
138.
106.
126.
135.
132.
139.
149.
151.
141.
185.
266.
208.
41.
20.
201.
316.
314.
257.
152.
146.
142.
134.
140.
155.
SOWS
M/S
.366
.454
.209
.274
.401
.876
1.267
1.280
1.032
.705
.475
.538
.531
.326
.522
.703
.902
.760
.729
.737
.912
.881
.709
.579
.555
.806
.809
.853
.470
.811
.426
.543
.558
.330
.248
.142
.197
.226
.260
.258
.312
.333
.309
.315
.364
.648
.549
.535
.649
.570
.423
.340
.360
.320
.171
.228
.274
.133
SDWD
DEC
12.5
15.6
14.8
15.5
29.6
25.2
14.1
18.4
32.5
41.4
20.8
20.3
14.7
19.6
37.6
33.7
21.4
20.2
16.5
17.4
16.2
16.7
16.9
19.1
23.6
25.1
32.0
37.1
46.9
29.8
43.7
37.4
21.9
8.4
6.6
9.1
9.8
7.9
8.2
8.7
14.4
13.4
12.2
29.1
13.0
21.9
13.5
16.5
17.6
15.9
22.1
37.4
24.2
12.4
13.2
16.5
7.5
6.5
SDEPA
DEC
16.8
29.4
74.3
23.3
68.6
26.4
15.0
19.0
45.9
52.8
24.9
25.1
20.6
41.5
55.4
37.5
29.0
22.5
24.3
24.7
22.3
20.2
23.0
21.7
26.7
30.6
36.0
40.5
70.0
33.7
65.0
80.2
30.9
11.1
15.8
18.3
17.3
9.0
11.0
10.4
16.1
15.1
14.7
53.5
29.0
26.5
16.9
19.2
24.9
19.1
24.6
71.6
41.8
23.0
20.5
22.9
16.2
9.2
TEMP
°C
8.6
8.7
9.1
9.0
9.2
9.1
8.9
8.6
8.3
7.5
6.7
6.8
6.9
5.4
6.7
7.2
7.7
8.5
10.6
11.8
13.0
13.0
13.9
12.6
10.9
9.6
9.0
8.2
7.9
7.4
6.3
5.8
4.3
1.7
2.1
2.7
3.3
3.1
2.6
2.1
1.9
2.3
4.3
8.6
10.8
14.9
15.9
15.2
12.3
10.0
8.9
6.8
5.6
4.1
2.8
2.0
1.5
1.3
DTDZ
°C
-.23
0.00
.04
.04
.03
.08
.08
.10
.23
.57
1.11
.85
.86
1.34
.61
.15
-.22
-.70
-1.91
-2.64
-2.97
-2.26
-2.78
-1.58
-.38
.25
.32
.52
.49
.55
.99
.94
.49
.61
.18
.08
-.17
-.22
-.25
-.31
-.35
-.43
-.91
-2.06
-1.08
-3.15
-3.84
-3.12
-1.02
.28
.61
1.71
1.89
.93
1.31
1.16
.58
1.22
SOLRAD
W/MA2
14.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
30.
53.
102.
312.
438.
420.
379.
284.
137.
33.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
22.
80.
167.
389.
458.
449.
408.
297.
163.
35.
0.
0.
0.
0.
0.
0.
0.
0.
0.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
63

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S	PEG  PEG    °C    °C   W/M"2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
306
306
306
306
306
306
306
306
306
306
306
306
306
306
306
306
306
306
306
306
306
306
307
307
307
307
307
307
307
307
307
307
307
307
307
307
307
307
307
307
307
307
307
307
307
307
308
308
308
308
308
308
308
308
308
308
308
308
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
1.6
1.7
1.9
1.0
1.6
.9
1.5
1.3
.9
1.0
.7
2.1
1.1
.7
.5
1.1
1.0
.9
1.6
1.2
.7
1.4
2.4
2.4
2.4
2.7
3.0
3.8
4.3
4.6
4.6
5.1
5.9
5.5
4.5
4.8
5.4
5.8
4.8
4.4
5.2
4.5
4.2
3.7
4.7
4.9
5.9
5.0
4.1
3.3
2.0
2.6
2.5
2.5
3.0
3.0
3.6
5.0
141.
133.
132.
100.
131.
147.
146.
150.
152.
163.
205.
286.
268.
225.
176.
290.
264.
113.
139.
156.
145.
152.
130.
122.
144.
166.
179.
173.
183.
198.
193.
188.
199.
197.
192.
201.
212.
212.
198.
197.
206.
198.
177.
169.
178.
194.
207.
224.
228.
217.
167.
142.
153.
153.
168.
182.
200.
235.
.143
.238
.279
.180
.215
.155
.238
.319
.258
.281
.266
.289
.182
.144
.154
.334
.214
.139
.246
.216
.202
.221
.379
.358
.573
.873
.941
1.009
1.182
1.317
1.309
1.297
1.424
1.329
1.157
1.127
1.230
1.260
1.230
1.162
1.177
1.050
1.055
.953
1.131
1.276
1.586
1.233
1.058
.968
.620
.418
.426
.537
.668
.772
.853
1.032
4.5
7.1
8.5
8.2
6.2
9.6
9.1
19.4
19.2
18.2
25.6
7.1
10.2
12.7
20.7
23.9
14.3
6.4
7.4
15.1
17.6
7.8
7.0
8.5
12.8
16.7
15.9
13.0
13.8
13.9
14.4
12.5
11.6
11.8
13.4
11.6
11.5
10.6
12.8
12.9
11.3
10.9
12.0
12.2
11.1
13.2
12.2
13.6
14.5
25.0
21.3
8.6
9.3
11.7
13.6
15.0
13.3
11.6
8.9
10.6
13.2
23.9
18.1
18.7
25.5
34.1
42.2
22.5
85.7
11.5
14.1
28.3
89.7
43.3
31.4
26.9
12.9
38.2
81.7
29.1
8.8
15.3
15.6
21.3
16.8
13.9
16.8
14.4
14.7
13.7
12.5
12.3
13.9
12.0
12.4
11.8
14.2
13.5
16.5
18.3
13.0
13.6
12.0
14.3
12.7
18.7
21.7
42.9
33.9
11.3
11.7
22.0
17.4
18.2
17.2
14.0
.4
.3
.4
.9
1.6
1.0
1.8
2.4
4.9
7.2
9.4
8.9
9.1
9.3
9.4
9.3
9.1
8.6
8.5
8.5
8.4
8.5
8.9
9.8
10.9
11.6
12.2
12.3
12.5
12.7
12.9
13.2
13.2
13.5
13.8
14.0
14.4
14.4
14.1
13.9
13.4
12.6
12.4
12.0
11.7
11.8
12.1
12.4
12.5
12.0
11.7
10.9
10.6
10.1
10.7
11.6
12.4
13.5
1.20
.66
.16
.21
-.14
-.23
-.46
-.45
-.70
-.57
-.99
-.26
-.19
-.11
.04
.07
.15
.40
.04
.06
.64
.34
.09
.21
.16
.06
0.00
.04
.01
.01
-.04
-.07
-.12
-.04
-.06
0.00
-.07
-.08
-.05
.02
-.01
.08
.08
.05
.02
.09
.09
.11
.14
.30
.22
.20
.09
.18
-.05
-.09
-.25
-.50
0.
0.
0.
0.
1.
36.
96.
155.
204.
244.
226.
81.
51.
22.
8.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
19.
26.
75.
87.
47.
50.
65.
129.
65.
20.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
38.
97.
138.
228.
387.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.01
.03
.10
.06
.05
.01
.03
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      64

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
315
315
315
315
315
315
316
316
316
316
316
316
316
316
316
316
316
316
316
316
316
316
316
316
316
316
316
316
316
316
317
317
317
317
317
317
317
317
317
317
317
317
317
317
317
317
317
317
317
317
317
317
317
317
318
318
318
318
HR
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
WS
M/S
2.2
3.4
3.7
1.7
1.5
2.0
3.0
3.4
1.7
2.4
1.9
1.2
1.1
1.4
1.1
1.0
1.6
1.4
2.1
1.1
.9
.9
1.7
1.3
2.1
2.6
2.2
1.6
2.3
2.4
1.6
1.0
1.6
1.8
2.6
4.1
4.2
3.7
3.2
5.6
4.5
3.6
4.0
4.4
5.2
4.7
4.2
3.5
3.0
2.4
2.7
2.7
2.0
2.2
2.1
2.1
2.4
2.2
WD
DEC
17.
7.
67.
160.
184.
208.
28.
44.
48.
42.
66.
78.
135.
100.
99.
176.
111.
41.
75.
82.
170.
191.
180.
234.
133.
137.
131.
142.
184.
154.
134.
135.
122.
124.
145.
157.
155.
166.
206.
199.
203.
178.
178.
198.
216.
208.
193.
185.
166.
178.
191.
149.
160.
167.
148.
149.
123.
128.
SOWS
M/S
.723
.860
.982
.580
.501
.671
1.011
.957
.682
.812
.619
.396
.187
.384
.340
.346
.570
.500
.506
.319
.256
.248
.298
.219
.187
.365
.350
.274
.505
.454
.277
.320
.208
.332
.510
.827
.871
.912
.882
1.472
1.135
.970
1.003
1.163
1.127
1.073
1.024
.790
.685
.850
.879
.748
.657
.511
.320
.293
.300
.307
SDWD SDEPA
DEC DEC
17.0
13.3
13.5
26.6
19.6
18.1
16.4
13.3
21.6
21.6
19.5
19.5
9.8
14.3
18.5
28.0
20.4
22.7
19.3
21.5
17.4
13.8
9.3
9.1
8.2
6.2
6.8
8.1
11.5
9.9
9.9
28.1
7.0
9.4
9.0
10.0
10.3
11.9
13.8
13.1
12.5
16.8
13.6
13.9
11.3
12.8
11.3
10.9
11.9
22.5
21.0
16.8
19.0
13.7
7.8
7.6
6.6
7.1
18.0
13.5
14.9
34.6
24.4
20.8
19.9
14.5
24.4
25.1
20.9
38.0
17.2
40.4
62.9
47.6
31.4
33.2
24.2
41.6
34.0
27.0
27.7
16.1
12.6
10.4
9.8
19.4
14.0
24.5
12.9
47.7
11.8
19.3
16.1
10.9
11.2
12.4
31.4
15.3
24.3
17.7
15.7
18.2
13.2
17.5
12.9
16.3
14.9
29.7
27.1
30.7
26.9
22.2
10.8
16.4
12.0
10.0
TEMP
°C
7.4
7.3
7.1
6.8
6.7
6.7
6.3
6.1
5.6
5.1
4.9
4.9
5.0
5.0
5.8
6.5
8.0
8.4
9.2
8.4
8.6
8.2
7.7
7.0
5.3
5.4
5.3
5.5
5.9
5.9
5.4
5.5
4.2
5.4
6.4
7.3
7.5
7.3
6.9
7.2
6.9
8.5
9.0
8.3
9.4
9.4
8.5
8.0
7.6
7.8
7.9
7.2
7.1
6.8
5.8
5.3
4.7
4.7
DTDZ SOLRAD
°C W/M"-2
.05
.05
.14
.09
.03
.03
.14
.17
.08
.08
.13
.04
.09
.37
.11
-.42
-1.20
-1.15
-1.52
-.59
-.41
-.11
.15
.45
.79
.16
.13
.15
0.00
.05
.35
.49
1.42
.49
.14
.11
.06
.17
.19
.00
-.08
-.50
-.39
.24
-.23
-.09
.04
.08
.11
.10
.11
.25
.29
.37
.89
.95
1.39
1.27
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
6.
129.
164.
197.
225.
225.
140.
122.
61.
7.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
7.
44.
143.
421.
246.
154.
190.
85.
8.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
PCPN
IN
.09
.09
.10
.08
.08
.12
.12
.11
.10
.08
.04
.03
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.02
.16
.04
.02
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
68

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG     M/S    PEG  PEG    °C    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
318
318
318
318
318
318
318
318
318
318
318
318
318
318
318
318
318
318
318
318
319
319
319
319
319
319
319
319
319
319
319
319
319
319
319
319
319
319
319
319
319
319
319
319
320
320
320
320
320
320
320
320
320
320
320
320
320
320
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
2.0
2.1
1.9
1.6
1.8
1.5
1.7
1.3
1.4
1.6
.9
2.0
2.0
1.5
1.4
.8
.4
.9
.4
.8
.4
.6
.9
1.4
.9
.9
2.1
1.0
1.1
1.0
1.2
2.4
2.3
2.8
2.5
1.1
.9
.7
.9
.8
1.0
2.2
1.9
1.1
2.1
1.7
1.6
1.3
.7
1.2
1.8
.7
.7
.8
.3
.3
.9
.6
127.
123.
116.
111.
130.
162.
188.
192.
203.
206.
219.
45.
55.
49.
79.
127.
109.
137.
170.
158.
173.
197.
105.
101.
144.
224.
146.
111.
164.
153.
156.
17.
152.
230.
337.
236.
183.
112.
206.
218.
300.
147.
169.
170.
140.
143.
127.
202.
162.
145.
125.
226.
169.
189.
99.
117.
155.
172.
.233
.256
.272
.268
.285
.412
.460
.523
.454
.449
.370
.465
.360
.386
.293
.173
.138
.149
.130
.176
.172
.150
.349
.451
.292
.331
.375
.154
.205
.219
.467
.698
.646
.631
.559
.363
.320
.231
.262
.311
.256
.309
.373
.301
.306
.332
.230
.276
.178
.225
.396
.198
.186
.199
.133
.181
.210
.226
5.9
6.4
7.9
7.2
10.7
17.0
19.6
29.8
28.9
27.5
35.6
14.0
9.7
13.8
11.1
13.5
21.5
10.4
25.2
12.9
31.8
21.3
36.0
21.6
21.1
29.9
11.2
11.1
12.0
15.4
25.0
16.9
17.1
12.8
12.9
24.4
23.8
20.8
17.2
27.9
16.5
7.7
18.3
30.2
6.9
10.3
11.7
24.7
16.9
13.4
12.9
18.9
21.1
19.5
29.5
25.5
15.1
23.6
8.1
7.5
13.3
9.8
14.4
33.4
28.4
36.6
49.1
42.2
60.0
16.0
10.8
22.9
15.3
34.1
48.9
22.5
59.0
58.6
79.7
46.3
59.4
89.8
59.0
48.0
13.2
31.2
33.0
30.0
93.3
18.5
22.6
20.5
18.3
27.4
30.5
39.1
30.5
97.5
24.4
16.4
40.0
86.3
13.5
13.9
21.5
55.7
44.9
27.4
24.6
74.2
48.3
53.1
33.2
59.4
37.4
51.5
4.4
4.4
5.3
5.6
6.2
8.2
9.1
9.7
10.6
11.2
11.0
10.0
8.6
7.8
7.4
6.7
5.3
4.8
4.1
4.3
4.6
5.0
5.4
5.7
4.8
5.3
3.9
2.7
4.1
5.2
8.4
11.1
11.7
10.7
9.5
9.3
8.9
8.4
7.7
7.3
8.2
7.3
6.9
7.1
7.2
7.4
7.5
7.7
7.6
7.5
7.4
7.8
8.3
8.7
9.8
10.0
10.1
10.4
1.61
1.31
.56
.34
.04
-.73
-.84
-.96
-1.21
-1.40
-1.08
-.69
.40
.75
.84
1.20
1.83
1.51
1.68
.87
.56
.45
.42
.19
.44
.57
.33
1.27
.06
-.31
-1.41
-2.79
-2.50
-1.57
-.51
-.36
-.04
.31
.61
.57
.14
.03
.06
.19
.07
-.02
.01
0.00
.04
.03
0.00
.04
-.12
-.25
-.57
-.32
-.24
-.27
0.
0.
0.
4.
70.
284.
350.
320.
397.
462.
210.
49.
11.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
14.
69.
124.
302.
342.
326.
188.
93.
34.
5.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
21.
57.
64.
49.
45.
23.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      69

-------
YEAR DAY HR   WS  WD
             M/S PEG
SDWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
 M/S   PEG  PEG    °C    °C   W/MA2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
320
320
320
320
320
320
320
320
320
320
321
321
321
321
321
321
321
321
321
321
321
321
321
321
321
321
321
321
321
321
321
321
321
321
322
322
322
322
322
322
322
322
322
322
322
322
322
322
322
322
322
322
322
322
322
322
322
322
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
1
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
.9
1.2
1.0
1.1
.6
1.0
1.3
1.2
1.6
1.1
1.5
2.6
1.7
2.7
2.0
2.8
1.8
1.7
.9
1.1
.6
.9
.8
.8
1.2
1.6
1.4
.5
.7
1.9
1.6
1.1
1.3
1.7
1.2
1.4
1.5
1.2
1.3
1.3
1.0
.4
2.0
1.5
.9
1.1
1.6
2.4
1.8
2.8
2.1
1.0
.8
1.5
1.1
.9
1.3
2.2
112.
27.
114.
195.
261.
298.
302.
325.
134.
174.
304.
202.
201.
145.
232.
127.
37.
293.
161.
26.
223.
244.
255.
274.
287.
136.
179.
223.
90.
114.
133.
119.
144.
127.
122.
148.
137.
131.
131.
101.
152.
185.
142.
127.
140.
231.
272.
291.
282.
303.
318.
307.
304.
124.
142.
187.
154.
139.
.232
.301
.229
.295
.229
.218
.239
.351
.498
.385
.625
.992
.595
.777
.812
.691
.592
.451
.349
.290
.193
.265
.278
.218
.268
.375
.393
.169
.159
.313
.296
.238
.218
.290
.250
.301
.265
.238
.220
.290
.251
.132
.387
.298
.239
.266
.273
.350
.271
.440
.330
.216
.189
.213
.168
.200
.303
.300
18.6
12.6
12.9
17.3
19.8
10.1
12.1
18.0
27.2
21.0
29.7
21.0
28.8
17.3
28.2
15.1
19.7
16.7
30.1
16.8
26.8
23.4
21.6
15.5
19.6
23.6
23.5
31.5
14.1
8.2
9.6
11.5
10.7
9.2
11.4
10.7
10.1
14.2
13.4
11.9
13.8
25.9
7.7
10.2
21.1
15.0
11.4
8.2
8.1
7.1
8.3
13.8
21.9
11.1
9.4
18.1
14.2
6.1
26.6
17.3
42.0
98.7
69.7
25.7
19.4
26.1
45.7
57.1
36.7
28.7
59.0
24.8
42.8
18.3
22.1
24.0
42.7
20.5
79.1
41.5
37.3
23.2
33.7
38.4
58.0
50.9
30.9
12.8
15.5
25.9
28.6
21.6
33.1
18.9
16.8
21.9
20.7
17.7
37.1
68.1
12.5
16.6
48.2
27.2
20.6
11.6
9.5
10.4
11.0
22.6
31.7
28.3
20.1
81.6
24.2
7.9
9.9
9.0
8.7
8.8
8.8
8.8
8.9
9.1
9.2
9.4
9.4
9.3
9.1
8.9
8.6
8.4
8.2
8.3
8.4
8.8
9.0
9.2
9.6
9.7
9.7
9.6
9.0
9.1
9.1
9.0
8.9
8.9
9.0
8.9
9.1
9.1
9.0
8.9
8.8
8.4
8.3
8.4
8.5
8.8
10.2
11.3
11.1
11.3
11.5
11.0
10.2
9.2
8.4
7.6
7.1
6.8
7.4
7.1
-.33
-.21
-.06
.08
.02
0.00
.01
.02
.12
.12
.06
.04
.16
.09
.01
.03
.09
-.02
-.13
-.39
-.25
-.24
-.32
-.26
-.20
-.14
-.09
-.04
.01
-.05
-.03
-.04
-.08
-.04
.04
-.08
-.08
-.09
-.10
-.15
-.10
-.11
-.25
-.45
-.71
-.88
-.59
-.49
-.48
-.28
-.05
.42
.60
.82
.59
.56
.05
.04
10.
4.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
11.
30.
47.
62.
71.
108.
75.
31.
14.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
9.
45.
69.
223.
301.
276.
306.
202.
112.
9.
0.
0.
0.
0.
0.
0.
0.
.00
.06
.15
.11
.08
.02
.02
.03
.03
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      70

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
323
323
323
323
323
323
323
323
323
323
323
323
323
323
323
323
323
323
323
323
323
323
323
323
324
324
324
324
324
324
324
324
324
324
324
324
324
324
324
324
324
324
324
324
324
324
324
324
325
325
325
325
325
325
325
325
325
325
HR
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
WS
M/S
1.3
1.0
1.6
2.7
2.3
2.3
1.0
1.5
2.4
1.1
1.4
3.6
2.7
2.2
2.1
2.7
2.3
.9
1.0
1.1
.6
.4
.5
.6
.5
.5
.6
1.3
.8
.5
1.1
1.7
1.7
1.7
2.3
1.7
3.4
2.8
2.5
1.6
2.0
2.0
1.9
2.5
2.5
2.5
2.3
2.4
2.4
2.6
3.2
3.5
2.8
1.2
2.3
2.1
1.2
1.5
WD
DEC
116.
178.
199.
136.
132.
141.
105.
127.
136.
162.
284.
244.
212.
153.
134.
135.
129.
117.
126.
132.
139.
180.
147.
208.
160.
153.
160.
167.
135.
154.
179.
120.
141.
153.
156.
232.
272.
259.
267.
253.
213.
235.
208.
178.
140.
124.
137.
166.
171.
247.
244.
304.
301.
278.
330.
331.
255.
151.
SDWS
M/S
.244
.283
.323
.493
.333
.419
.279
.266
.350
.264
.372
.575
.536
.407
.304
.411
.383
.300
.241
.205
.156
.095
.125
.173
.101
.136
.159
.274
.182
.180
.239
.259
.314
.404
.471
.362
.705
.662
.473
.452
.522
.532
.539
.751
.439
.323
.467
.748
.755
.701
.625
.686
.491
.288
.538
.588
.559
.507
SDWD
DEC
12.4
24.7
13.5
7.4
7.5
9.1
15.7
9.8
7.3
19.9
23.6
8.3
10.6
9.8
7.0
6.8
7.5
24.7
20.9
11.3
17.0
22.1
20.0
16.6
15.2
21.3
21.3
8.6
23.9
24.3
23.7
7.5
11.6
11.4
11.6
14.7
12.3
12.9
10.7
16.2
15.6
15.7
23.0
16.5
8.3
6.4
11.5
15.8
22.2
13.2
9.4
11.1
8.9
14.5
13.3
20.6
35.9
21.9
SDEPA
DEC
30.5
87.8
27.7
8.3
10.6
13.1
21.7
14.7
9.1
52.9
40.0
17.7
14.5
24.7
9.4
8.6
11.3
87.4
29.2
17.7
76.6
97.8
62.9
81.3
48.5
70.8
56.7
22.6
46.9
53.9
50.0
10.6
21.2
14.7
19.7
28.0
15.5
17.2
13.2
19.4
22.0
21.9
31.4
20.7
15.7
7.0
17.6
30.7
24.3
20.4
14.4
27.6
10.6
55.5
21.0
25.0
48.5
25.8
TEMP
°C
6.9
8.1
9.0
8.2
8.3
8.5
8.5
8.6
9.0
9.6
10.4
10.6
11.1
10.7
10.7
10.8
10.8
10.6
10.3
10.2
9.8
9.6
9.3
9.5
9.2
9.1
9.0
9.0
8.6
8.6
8.9
8.9
9.4
10.3
11.9
12.2
12.5
12.5
12.3
12.3
12.3
11.9
11.5
11.4
10.9
10.5
10.7
11.3
11.6
11.5
11.2
10.2
9.2
9.0
8.9
8.4
8.4
8.8
DTDZ
°C
.43
.25
.05
-.07
.06
.08
.21
.19
.04
0.00
-.09
-.07
-.01
-.03
-.02
-.01
.34
.55
.50
.17
.39
.59
.72
.16
.34
.31
.37
.05
.02
.03
-.04
-.14
-.24
-.38
-.53
-.33
-.14
-.08
.01
.06
.06
.10
.08
.03
.01
0.00
.08
.14
.10
.09
.06
0.00
-.04
-.04
.01
0.00
-.08
-.36
SOLRAD
W/NT2
0.
0.
0.
0.
0.
0.
0.
3.
14.
41.
82.
91.
50.
23.
12.
11.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
5.
94.
176.
250.
146.
94.
66.
20.
7.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
26.
79.
PCPN
IN
.00
.00
.00
.00
.00
.01
.02
.03
.02
.01
.00
.00
.00
.00
.01
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.01
.02
.00
.00
.00
.00
.00
.00
.02
.00
.00
.00
.00
.00
71

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
325
325
325
325
325
325
325
325
325
325
325
325
325
325
326
326
326
326
326
326
326
326
326
326
326
326
326
326
326
326
326
326
326
326
326
326
326
326
327
327
327
327
327
327
327
327
327
327
327
327
327
327
327
327
327
327
327
327
HR
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
WS
M/5
1.8
1.8
2.3
3.3
4.1
2.4
2.2
1.8
2.3
2.6
2.4
3.9
2.8
1.6
1.3
1.2
1.6
1.8
1.5
.7
1.1
1.5
1.4
.8
1.3
1.1
1.4
2.1
2.1
2.0
4.1
2.9
1.4
1.9
1.8
1.4
1.2
1.6
1.7
2.1
2.6
2.7
1.0
1.6
1.7
2.1
1.9
5.5
4.2
4.4
4.7
4.3
3.4
4.2
4.6
3.9
3.5
2.6
WD
DEC
100.
74.
42.
181.
92.
237.
340.
98.
41.
93.
18.
12.
22.
115.
141.
126.
67.
78.
72.
45.
26.
131.
171.
139.
127.
286.
265.
149.
160.
144.
131.
129.
184.
141.
151.
130.
130.
154.
118.
151.
125.
145.
200.
156.
136.
129.
190.
210.
190.
185.
203.
248.
210.
197.
194.
185.
166.
168.
SOWS
M/S
.583
.663
.768
.898
1.023
.722
.727
.613
.587
.595
.810
.991
.940
.535
.193
.441
.512
.402
.428
.279
.383
.363
.262
.257
.370
.392
.349
.461
.397
.311
.726
.515
.312
.306
.321
.233
.206
.259
.271
.349
.407
.522
.392
.513
.298
.426
.584
1.181
1.082
.970
.966
1.187
.750
.973
1.049
.828
.710
.617
SDWD
DEC
19.5
20.4
19.4
14.5
12.7
17.8
22.0
18.6
13.2
11.3
18.1
13.3
19.1
25.7
13.8
35.5
19.1
13.9
19.0
22.0
23.5
22.9
10.3
24.1
19.6
28.9
22.4
13.2
11.1
9.9
6.9
8.5
12.2
10.4
8.5
9.8
8.6
10.8
9.9
13.3
13.4
14.9
22.7
23.9
16.4
8.6
18.2
10.1
11.6
11.6
10.8
11.2
10.9
11.4
11.4
10.5
10.2
11.2
SDEPA
DEC
23.9
25.9
22.1
18.3
14.2
18.7
25.7
22.0
14.9
12.6
20.0
13.5
21.7
61.7
16.9
53.2
25.0
18.2
26.9
35.3
27.7
51.9
13.1
68.4
28.1
51.8
35.5
19.8
14.0
16.9
8.0
11.0
16.7
21.6
18.3
19.1
15.2
26.0
12.3
27.9
20.5
25.9
77.4
85.8
44.4
10.2
26.5
12.4
12.4
13.9
11.8
25.4
16.8
14.2
12.5
13.5
14.1
12.2
TEMP
°C
9.5
10.4
12.4
12.5
12.5
11.6
9.3
7.9
7.3
7.0
6.5
6.6
6.4
5.5
4.5
6.2
6.4
6.1
5.5
5.6
5.9
5.2
4.9
5.8
6.6
6.9
7.5
8.2
7.7
7.5
5.4
4.7
4.5
4.2
3.8
3.0
3.0
3.4
3.5
4.0
4.8
5.4
5.6
6.4
6.7
7.6
8.9
10.1
10.1
11.1
11.8
9.4
9.6
9.5
8.9
8.5
7.9
7.6
DTDZ
°C
-.67
-.92
-2.37
-2.49
-2.50
-1.73
-.13
.56
.63
.50
.53
.40
.49
.52
1.06
.17
-.09
-.20
-.36
-.32
-.24
-.25
-.17
-.46
-.95
-.67
-.73
-1.16
-.71
-.76
-.08
.11
.07
.01
.29
.79
.48
-.07
-.12
-.01
.08
.05
-.05
.16
.32
.31
.28
.12
-.01
-.12
-.21
.13
.03
0.00
.04
.10
.15
.12
SOLRAD
W/MA2
117.
175.
322.
280.
212.
94.
7.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
28.
69.
93.
176.
302.
262.
182.
72.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
9.
54.
115.
191.
213.
63.
79.
49.
1.
0.
0.
0.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.08
.12
.04
.03
.02
.02
.00
.00
.00
.07
.00
.00
.00
.00
.00
.00
72

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG     M/S    PEG  PEG    °C    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
327
327
327
327
328
328
328
328
328
328
328
328
328
328
328
328
328
328
328
328
328
328
328
328
328
328
328
328
329
329
329
329
329
329
329
329
329
329
329
329
329
329
329
329
329
329
329
329
329
329
329
329
330
330
330
330
330
330
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
3.0
1.8
2.1
2.6
2.9
2.1
2.1
3.4
3.1
2.4
3.1
2.5
2.1
2.2
3.0
4.4
4.5
3.4
3.2
4.2
3.3
3.4
2.6
1.6
1.4
1.6
1.6
1.8
1.6
1.9
1.7
2.2
2.4
1.8
2.2
1.5
1.8
1.4
1.3
2.1
1.5
1.6
1.2
1.6
.8
.9
.7
.8
1.5
1.5
1.3
2.6
2.8
2.5
2.2
1.9
1.4
1.7
181.
158.
152.
167.
167.
220.
238.
225.
137.
139.
123.
126.
108.
126.
172.
187.
211.
199.
170.
166.
168.
147.
125.
104.
105.
213.
123.
136.
117.
122.
106.
125.
123.
107.
125.
125.
305.
341.
327.
286.
214.
247.
271.
130.
99.
286.
162.
205.
202.
169.
161.
217.
130.
136.
129.
138.
156.
191.
.655
.452
.437
.699
.776
.528
.390
.633
.478
.435
.459
.363
.403
.506
.707
1.011
1.041
.802
.918
.920
.789
.718
.454
.391
.308
.450
.309
.321
.270
.247
.347
.316
.268
.253
.294
.310
.465
.324
.343
.317
.345
.319
.412
.373
.288
.236
.252
.172
.301
.310
.231
.539
.482
.497
.388
.295
.381
.598
12.5
19.2
11.7
14.0
11.9
16.5
10.7
11.1
8.2
10.5
8.1
7.1
11.7
12.9
11.3
11.8
10.6
11.6
14.9
11.5
12.8
10.2
8.9
12.2
14.1
27.6
16.0
10.6
10.2
6.5
14.3
7.1
5.5
9.1
5.7
15.8
11.8
13.2
14.6
9.4
18.3
12.3
23.8
13.0
26.7
33.5
28.3
10.6
11.2
10.3
9.1
12.0
7.8
9.3
9.3
8.4
17.5
18.3
26.7
57.5
20.0
20.7
12.4
47.2
20.5
20.2
17.2
16.9
10.5
7.8
17.6
20.2
12.3
17.5
12.8
12.2
18.1
12.4
14.1
16.1
10.0
21.0
17.7
74.1
20.2
17.8
12.0
8.4
16.7
7.6
6.0
16.9
6.3
20.9
21.5
16.8
21.7
12.8
41.3
29.1
39.9
19.8
90.7
62.3
88.2
56.8
25.7
18.6
24.6
27.7
12.5
10.4
10.8
12.4
33.3
28.2
7.7
7.4
6.6
6.7
7.0
6.8
6.6
5.7
4.8
4.6
4.5
4.3
4.9
7.3
8.4
8.5
7.3
6.2
5.9
6.1
6.2
5.4
4.7
4.3
5.1
5.2
4.9
5.2
5.0
4.2
4.0
4.0
3.4
3.3
4.7
5.1
5.8
7.2
8.1
8.0
9.5
9.1
8.7
8.4
7.8
7.6
7.0
6.8
6.4
5.6
5.1
4.6
4.4
4.4
4.4
4.7
5.4
5.7
.06
.04
.35
.20
.15
.13
.07
.04
.03
.06
.22
.35
.48
-.38
-.09
-.04
.06
.02
.07
.04
.11
.29
.60
1.03
.97
.18
.49
.30
.62
1.40
1.42
1.22
1.45
1.84
.80
.60
.13
-.63
-.62
-.32
-.76
-.41
-.33
-.21
.08
.15
.16
.08
.04
.14
.14
.14
.07
-.03
.02
.22
.14
.05
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
6.
35.
242.
135.
76.
41.
20.
59.
44.
5.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
10.
55.
142.
290.
229.
188.
109.
74.
28.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.08
.02
.02
.02
.00
.00
.00
.00
.00
.02
.12
.03
.00
.00
.00
.00
.00
.00
.06
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.03
.06
.10
.08
.07
.08
.01
.00
.00
.00
.00
.00
                                       73

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
330
330
330
330
330
330
330
330
330
330
330
330
330
330
330
330
330
330
331
331
331
331
331
331
331
331
331
331
331
331
331
331
331
331
331
331
331
331
331
331
331
331
332
332
332
332
332
332
332
332
332
332
332
332
332
332
332
332
HR
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
WS
M/S
1.4
1.8
2.1
3.1
3.7
4.3
5.4
5.8
6.3
4.8
3.0
2.2
2.0
2.1
2.1
2.2
1.3
1.3
1.0
1.0
.8
.5
1.0
1.4
1.3
1.1
1.0
1.9
1.1
.6
2.3
2.4
.9
.7
1.5
.6
.7
.7
1.3
1.5
.9
.7
1.4
1.9
1.0
.9
1.0
1.2
1.5
2.8
1.9
.6
.9
1.0
1.9
1.2
1.7
1.4
WD
DEC
181.
181.
206.
211.
220.
237.
252.
250.
251.
244.
225.
150.
144.
173.
113.
122.
117.
159.
181.
196.
170.
249.
151.
110.
143.
144.
159.
140.
191.
234.
298.
317.
82.
194.
113.
139.
157.
127.
157.
116.
189.
180.
151.
122.
195.
154.
142.
157.
126.
127.
115.
54.
166.
227.
302.
280.
312.
303.
SOWS
M/S
.518
.539
.532
.658
.742
.765
.931
1.047
1.177
.965
.710
.451
.323
.521
.255
.320
.214
.309
.228
.191
.286
.166
.212
.228
.224
.187
.320
.348
.300
.216
.376
.424
.317
.162
.212
.154
.144
.203
.307
.187
.154
.268
.258
.310
.220
.156
.199
.250
.179
.426
.387
.219
.284
.239
.346
.282
.310
.212
SDWD
DEC
25.7
17.4
15.0
12.1
10.5
10.7
9.7
9.4
9.6
11.0
13.1
13.4
10.4
15.5
7.3
7.2
7.8
11.9
21.2
13.5
30.2
16.1
22.3
15.7
12.5
10.2
18.4
7.3
25.0
31.7
7.5
16.6
23.0
18.5
8.6
30.1
15.8
27.3
10.8
7.6
11.4
28.6
8.3
5.9
14.9
12.8
13.4
14.1
10.7
8.1
10.2
26.7
22.1
16.8
12.9
20.2
11.6
8.9
SDEPA
DEC
34.3
19.7
20.9
15.2
13.6
12.2
11.9
11.2
12.4
12.1
23.7
24.5
15.0
29.4
9.8
11.0
17.3
33.8
74.1
65.1
93.8
58.6
50.2
37.1
20.3
16.2
39.4
12.5
54.1
60.7
15.7
21.4
38.5
100.1
12.9
49.1
51.3
41.6
19.7
15.6
40.6
75.4
32.9
7.6
61.2
31.2
24.5
30.8
16.9
17.0
32.1
39.8
76.4
48.9
19.0
25.8
21.1
15.4
TEMP
°C
5.6
5.6
5.9
6.3
7.2
8.4
9.2
9.5
9.6
8.7
7.6
6.2
5.1
5.4
3.7
3.8
3.4
4.3
4.1
4.8
5.4
5.4
4.5
3.7
3.8
4.2
5.0
6.0
7.6
10.7
10.2
10.9
12.7
10.8
8.1
7.5
6.2
5.0
4.3
3.8
3.5
2.6
1.6
.9
1.3
.5
-.4
-.3
-.2
.7
1.5
3.6
5.7
8.2
8.8
10.4
11.0
10.6
DTDZ
°C
.03
.01
.01
-.04
-.18
-.36
-.40
-.34
-.45
-.19
.15
.59
.71
.37
1.78
1.66
1.83
1.23
1.12
.73
.53
.58
.68
.78
.59
.20
-.13
-.35
-.61
-1.05
-.36
-.53
-1.70
.16
1.98
1.61
1.47
1.73
1.05
1.20
.89
1.17
1.40
.94
.68
1.34
1.44
.76
.49
-.06
-.38
-1.13
-1.12
-1.42
-.51
-.69
-.57
-.04
SOLRAD
W/M-2
0.
2.
11.
50.
156.
242.
306.
252.
238.
78.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
45.
108.
213.
331.
275.
209.
142.
32.
5.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
43.
182.
303.
338.
319.
248.
192.
79.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
74

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S    PEG   PEG     °C    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
332
332
332
332
332
332
332
332
333
333
333
333
333
333
333
333
333
333
333
333
333
333
333
333
333
333
333
333
333
333
333
333
334
334
334
334
334
334
334
334
334
334
334
334
334
334
334
334
334
334
334
334
334
334
334
334
335
335
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
.6
1.0
1.5
1.4
1.2
.9
1.4
1.4
1.4
1.5
1.3
1.3
1.0
1.7
1.2
1.3
1.4
1.4
1.1
.6
.4
.6
1.3
1.2
1.1
.8
1.1
1.2
1.4
1.4
1.4
.8
1.0
1.8
1.2
.8
1.2
1.2
1.0
1.4
1.4
1.0
.8
.5
.9
1.2
1.9
1.4
.7
.7
.7
1.3
1.0
1.0
1.4
1.7
1.3
1.7
290.
130.
139.
116.
165.
123.
145.
146.
146.
147.
150.
146.
156.
139.
133.
136.
144.
137.
133.
155.
165.
246.
288.
313.
317.
270.
153.
138.
144.
135.
136.
149.
122.
137.
196.
174.
135.
142.
133.
153.
114.
133.
128.
181.
173.
212.
287.
287.
150.
133.
184.
139.
150.
151.
141.
138.
155.
142.
.135
.227
.183
.202
.283
.183
.224
.230
.167
.186
.224
.220
.148
.153
.148
.149
.159
.211
.240
.151
.171
.165
.191
.238
.232
.319
.312
.263
.200
.219
.224
.215
.229
.256
.230
.216
.206
.177
.132
.319
.207
.213
.170
.198
.237
.278
.295
.211
.192
.134
.208
.196
.129
.195
.202
.206
.185
.201
16.7
14.3
7.6
8.5
13.8
16.2
9.8
7.2
6.9
7.4
6.3
6.4
10.4
4.6
6.8
6.1
5.8
7.5
16.8
20.6
24.8
20.3
7.9
11.4
14.7
23.1
25.9
16.3
8.1
11.3
9.5
17.6
17.9
9.7
18.8
23.0
13.7
14.1
12.0
13.1
10.4
14.6
14.1
24.9
20.8
16.7
8.2
9.2
17.5
13.3
18.4
9.1
6.7
19.1
8.7
7.1
8.0
10.6
27.4
59.5
11.4
18.7
25.3
24.3
17.2
10.2
13.4
17.1
13.2
15.0
25.3
8.5
10.6
12.5
13.7
11.6
24.0
38.8
51.4
25.1
12.3
24.3
19.4
53.3
40.1
29.1
13.6
24.3
30.4
54.7
44.6
27.2
67.2
85.9
52.2
23.3
31.1
22.6
18.2
37.0
29.4
53.9
84.1
58.1
24.2
25.8
58.3
64.4
100.6
24.4
16.3
47.8
30.5
19.0
17.5
26.3
8.3
5.8
5.1
4.2
4.6
3.1
3.5
3.1
2.8
2.6
2.2
2.0
1.4
1.5
1.3
1.5
2.2
3.5
4.9
6.3
7.8
9.1
8.7
8.5
8.0
6.9
5.7
4.2
3.7
3.4
3.5
3.4
3.2
3.1
2.4
1.4
.7
.3
1.0
1.4
1.8
2.5
3.6
6.6
8.2
10.0
9.1
8.9
7.1
4.7
3.7
3.1
2.2
2.0
1.5
.7
.7
.3
.96
1.94
1.23
1.69
.68
1.56
.75
.70
.80
.66
.53
.55
1.16
.55
.82
.90
.41
-.27
-.49
-.44
-.60
-.77
-.16
.12
.40
.87
1.35
1.35
.78
.64
.59
.50
.57
.36
.81
1.37
.98
1.37
.79
.08
-.24
-.42
-.58
-1.52
-1.31
-1.61
-.49
-.16
1.17
2.24
1.99
1.25
1.46
.81
1.02
.79
.57
.54
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
40.
108.
147.
143.
162.
195.
113.
39.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
34.
72.
143.
255.
232.
220.
141.
61.
4.
0.
0.
0.
0.
0.
0.
0.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      75

-------
YEAR DAY HR   WS  WD
             M/S PEG
SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
 M/S   PEG  PEG    °C    °C   W/M^2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
335
335
335
335
335
335
335
335
335
335
335
335
335
335
335
335
335
335
335
335
335
335
336
336
336
336
336
336
336
336
336
336
336
336
336
336
336
336
336
336
336
336
336
336
336
336
337
337
337
337
337
337
337
337
337
337
337
337
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
1.1
.8
1.6
1.3
1.3
1.8
1.0
1.0
.8
.9
.8
1.7
1.3
1.5
.5
.5
.8
1.5
.7
.8
1.7
.9
1.3
1.3
.9
1.4
1.5
1.4
.9
1.2
1.1
1.9
1.5
3.7
4.1
2.0
2.1
1.0
.9
1.0
1.2
.8
2.3
2.1
1.7
2.2
1.9
1.1
2.6
3.9
2.2
1.1
1.3
.6
1.1
1.3
1.5
1.1
149.
169.
146.
123.
150.
135.
133.
146.
157.
176.
244.
283.
289.
287.
288.
196.
141.
138.
213.
143.
126.
211.
99.
155.
142.
149.
130.
167.
153.
221.
181.
147.
249.
267.
119.
153.
218.
112.
228.
194.
190.
139.
237.
234.
160.
153.
111.
90.
161.
199.
184.
162.
186.
155.
123.
122.
97.
178.
.236
.229
.235
.234
.193
.258
.200
.222
.186
.206
.184
.296
.244
.179
.213
.129
.142
.267
.185
.200
.198
.272
.179
.280
.270
.268
.288
.361
.389
.411
.301
.376
.322
.753
.788
.499
.646
.304
.337
.349
.287
.282
.591
.638
.478
.435
.299
.221
.525
.864
.601
.247
.297
.283
.219
.286
.347
.300
21.0
20.4
10.9
21.7
12.5
8.7
15.3
11.0
17.1
13.9
18.3
8.1
16.1
5.8
27.6
20.7
14.7
9.5
30.6
17.7
9.4
31.2
9.6
12.2
14.1
11.9
14.2
22.5
35.7
37.2
35.5
10.6
15.4
11.5
8.0
22.3
18.4
35.5
26.7
32.8
20.4
38.4
15.3
17.0
19.3
17.9
10.7
11.2
10.6
10.6
20.9
31.1
26.8
27.6
16.5
10.9
12.0
30.4
36.4
67.3
21.6
61.2
36.3
18.7
21.4
27.9
38.5
32.7
23.2
18.1
24.4
12.1
47.4
92.0
76.1
18.8
63.8
51.4
20.4
74.1
51.5
51.3
27.6
22.7
27.0
65.7
59.1
70.7
69.7
22.6
77.9
45.1
14.6
64.4
33.8
69.8
76.4
72.5
65.9
85.7
63.3
75.7
91.4
31.8
41.1
21.6
32.1
11.0
77.0
53.2
63.5
97.8
36.1
17.4
16.5
51.9
.5
.8
.9
1.3
1.9
1.9
2.4
5.5
6.5
8.7
10.7
10.1
10.2
10.4
9.0
7.0
6.6
6.1
5.2
4.6
4.1
4.4
3.9
3.3
3.5
4.1
4.6
4.9
5.3
6.0
6.2
6.6
7.1
8.2
7.6
7.2
7.4
7.3
7.4
7.5
7.7
7.7
7.9
8.2
8.2
8.1
8.1
8.5
10.9
13.0
12.7
11.7
12.0
11.6
11.5
11.6
12.2
12.4
.13
.37
.11
.09
.16
.03
.28
-.72
-.41
-.73
-1.27
-.37
-.04
.04
.81
1.75
2.18
1.09
1.17
1.43
1.07
.90
1.78
.91
1.18
.27
.14
.05
.32
.36
.17
-.11
-.09
.06
.10
.03
.02
.06
.07
.04
.15
.20
.05
.16
.34
.11
.35
1.11
.56
.29
.48
.88
.48
.50
.44
.21
.23
.15
0.
0.
0.
0.
0.
1.
40.
200.
140.
254.
294.
187.
99.
54.
4.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
22.
46.
51.
43.
22.
7.
4.
5.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
13.
31.
65.
75.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.02
.00
.00
.00
.00
.02
.12
.20
.21
.11
.13
.01
.01
.00
.17
.11
.02
.01
.00
.00
.00
.00
.00
.00
.00
.06
.04
.07
.03
.02
                                      76

-------
YEAR DAY  HR   WS  WD
              M/S PEG
SOWS  SDWD SDEPA   TEMP  DTDZ SOLRAD PCPN
 M/C    ntpr!  nfi-    °Q    op
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
337
337
337
337
337
337
337
337
337
337
337
337
338
338
338
338
338
338
338
338
338
338
338
338
338
338
338
338
338
338
338
338
338
338
338
338
339
339
339
339
339
339
339
339
339
339
339
339
339
339
339
339
339
339
339
339
339
339
13
14
15
16
17
18
19
20
21
22
23
24
'1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
1.2
2.1
1.4
1.6
.8
1.9
1.7
1.1
2.1
2.6
2.8
3.2
3.7
3.7
3.2
2.9
3.0
2.3
2.3
3.1
2.8
2.5
2.7
3.0
2.9
2.7
3.5
2.9
4.8
2.7
3.4
4.1
3.9
2.3
2.2
2.1
2.0
2.2
2.1
2.1
.9
.6
.6
.9
1.8
2.4
1.8
2.0
1.5
.9
.4
1.0
2.1
1.5
2.3
1.5
1.1
1.3
175.
137.
151.
144.
136.
116.
125.
138.
127.
130.
157.
171.
185.
190.
191.
192.
193.
194.
219.
217.
209.
236.
218.
199.
194.
159.
162.
180.
227.
188.
151.
178.
182.
162.
154.
167.
149.
141.
142.
140.
122.
148.
156.
143.
138.
143.
141.
166.
140.
143.
149.
284.
258.
169.
132.
160.
157.
216.
.340
.445
.337
.272
.211
.348
.344
.180
.279
.351
.501
.730
.874
.902
.908
.676
.732
.598
.592
.769
.778
.530
.635
.796
.762
.661
.765
.943
.939
.585
.613
.877
.896
.549
.393
.443
.322
.351
.270
.279
.348
.227
.181
.189
.275
.387
.361
.321
.288
.242
.138
.191
.315
.322
.327
.298
.248
.314
24.5
12.9
13.4
7.8
18.5
8.7
11.7
8.7
6.2
6.0
9.0
11.5
12.8
12.1
13.1
11.8
12.5
13.6
12.4
12.5
12.5
11.2
13.3
13.4
13.3
12.7
11.5
15.1
9.5
11.9
8.2
10.3
12.3
11.3
9.0
11.2
9.4
10.1
10.9
12.0
26.6
35.4
14.8
17. 7
8.5
7.1
9.9
7.1
9.6
13.7
28.3
15.8
7.1
11.9
6.3
11.8
18.9
21.4
53.1
24.9
28.0
19.9
40.0
11.8
23.8
30.5
7.3
9.3
11.0
12.4
14.0
12.5
13.4
12.1
13.8
14.9
15.5
13.7
15.3
13.2
16.5
15.4
18.4
14.0
14.5
34.2
10.9
44.5
13.8
11.8
13.9
22.1
16.5
21.0
11.0
12.9
14.8
52.8
70.0
58.8
55.2
28.7
15.9
8.8
11.7
13.3
18.5
21.3
43.2
41.4
24.3
27.8
8.5
25.9
51.3
73.3
12.5
12.6
12.5
12.2
11.8
12.3
12.6
12.0
12.6
12.9
13.9
15.2
15.4
15.1
14.7
14.6
14.4
14.3
14.1
14.3
14.4
14.3
14.4
14.7
14.7
14.5
14.1
13.5
13.4
12.6
12.4
12.6
12.3
11.5
10.8
10.2
9.4
9.2
9.2
8.5
7.8
7.1
6.9
6.7
7.0
8.4
10.3
11.4
12.9
13.2
12.8
12.2
11.8
11.3
10.9
10.1
9.8
9.3
.09
.14
.09
.19
.59
.84
.87
.69
.77
.51
.40
.29
.19
.13
.21
.13
.17
.08
.13
.22
.24
.41
.45
.16
.06
.15
.25
.25
.31
.25
.09
.13
.11
.41
.55
.57
.94
1.24
1.04
.95
1.59
1.26
1.25
.96
.21
-.24
-.54
-.26
-.49
-.41
-.05
.17
.12
.19
.28
.31
.36
.61
39.
33.
27.
9.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
5.
14.
26.
35.
32.
25.
17.
8.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
47.
132.
213.
212.
175.
133.
44.
14.
0.
0.
0.
0.
0.
0..
.05.
.01
.03
.02
.03
.01
.02
.04
.05
.04
.03
.00
.06
.09
.14
.16
.15
.17
.16
.09
.08
.10
.08
.08
.04
.03
.05
.18
.06
.03
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.00
                                       77

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
.1989
1989
1989
1989
1989
1989
DAY
339
339
340
340
340
340
340
340
340
340
340
340
340
340
340
340
340
340
340
340
340
340
340
340
340
340
341
341
341
341
341
341
341
341
341
341
341
341
341
341
341
341
341
341
341
341
341
341
341
341
342
342
342
342
342
342
342
342
HR
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
WS
M/S
1.0
1.0
2.0
1.4
1.4
1.3
2.2
1.0
1.0
1.8
1.5
1.5
1.4
1.8
1.6
1.7
1.8
1.5
.6
.8
.7
.7
1.1
.9
1.6
1.5
1.0
2.0
2.0
1.1
.7
.8
.9
2.2
1.2
1.1
.8
1.1
1.2
.7
.8
1.1
1.7
1.5
3.0
2.1
1.6
1.6
2.0
2.8
2.9
4.0
2.5
1.8
2.7
3.0
2.6
4.1
WD
DEC
162.
164.
149.
163.
160.
146.
192.
115.
158.
177.
171.
154.
175.
241.
292.
306.
157.
20.
111.
111.
68.
174.
307.
304.
82.
230.
241.
120.
137.
294.
233.
172.
154.
145.
139.
162.
130.
166.
132.
199.
107.
150.
132.
147.
114.
160.
133.
172.
179.
280.
182.
201.
179.
217.
218.
225.
201.
204.
SOWS
M/S
.232
.287
.333
.285
.312
.417
.521
.396
.409
.459
.347
.309
.323
.300
.310
.331
.415
.422
.209
.113
.181
.150
.260
.210
.279
.412
.307
.368
.453
.225
.195
.170
.188
.321
.204
.268
.220
.232
.314
.200
.185
.162
.311
.353
.568
.488
.386
.478
.459
.554
.908
1.201
.810
.530
.654
.684
.658
.848
SDWD
DEC
27.1
22.6
11.2
9.8
13.1
28.8
13.4
32.9
30.7
13.1
15.7
10.8
16.6
8.5
11.1
13.7
13.7
15.0
17.8
8.2
22.5
18.1
11.7
13.1
9.6
16.6
14.0
14.6
16.6
10.0
19.9
16.6
23.9
7.0
10.0
18.3
20.3
17.5
17.3
23.0
15.2
12.2
9.6
20.3
8.6
17.4
11.5
17.5
14.4
12.9
16.4
14.4
20.7
24.3
12.5
11.4
12.6
9.1
SDEPA
DEC
42.2
28.2
16.6
18.6
20.4
54.7
15.0
60.7
55.2
19.7
23.1
12.5
58.7
16.2
13.8
21.2
22.3
16.3
33.9
13.6
44.1
93.0
17.4
28.6
36.4
64.4
49.8
38.2
44.8
27.4
66.9
57.7
64.2
9.7
22.4
29.3
45.3
39.5
25.5
46.4
20.8
20.7
14.2
50.8
9.5
45.2
19.5
21.3
34.6
31.8
26.1
15.6
26.0
46.2
15.2
13.3
14.4
9.3
TEMP
°C
9.7
10.2
10.2
9.6
9.6
10.2
10.7
10.5
10.7
10.7
10.7
10.8
11.2
11.2
11.8
12.0
11.3
10.5
10.3
10.0
9.8
9.5
9.4
9.4
9.0
9.2
8.9
8.9
8.5
8.2
7.7
7.5
7.5
7.6
8.0
8.3
9.3
9.6
10.1
10.1
10.6
10.2
10.1
9.8
9.3
9.5
9.4
10.5
10.6
10.1
10.7
11.1
10.8
10.6
10.1
9.7
. 9.4
9.3
DTDZ
°C
.62
.23
.21
.26
.39
.35
.08
.22
.09
.05
-.03
-.17
-.23
-.16
-.20
-.28
-.37
-.10
.04
.13
.19
.40
.13
.07
.29
.12
.32
.46
.35
.28
.58
.58
.39
-.04
-.13
-.27
-.67
-.31
-.49
-.21
-.40
-.08
.05
.17
.44
.21
.17
.20
.21
.31
.44
.11
.08
.10
.19
.22
.22
.14
SOLRAD
W/M^2
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
23.
73.
61.
83.
135.
110.
20.
18.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
14.
75.
121.
78.
76.
54.
28.
8.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.06
.06
.08
.09
.01
.14
.10
.01
.00
.00
.00
.00
.00
.00
.00
78

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
342
342
342
342
342
342
342
342
342
342
342
342
342
342
342
342
343
343
343
343
343
343
343
343
343
343
343
343
343
343
343
343
343
343
343
343
343
343
343
343
344
344
344
344
344
344
344
344
344
344
344
344
344
344
344
344
344
344
HR
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
WS
M/R
2.9
2.7
2.9
4.2
4.0
5.6
5.7
5.2
4.0
3.1
3.6
3.9
3.9
3.8
4.2
4.2
3.3
1.7
2.3
2.0
2.8
3.1
2.8
1.3
2.2
2.1
2.5
1.9
1.2
1.6
2.5
1.5
1.8
1.2
1.4
.9
1.3
1.2
1.1
.8
.8
.8
.8
1.7
1.0
1.3
1.3
1.6
2.0
1.0
.6
.6
1.6
2.9
3.7
3.3
2.0
3.0
WD
DEC
208.
196.
234.
254.
231.
232.
231.
224.
191.
163.
180.
185.
187.
186.
197.
193.
194.
144.
222.
161.
135.
129.
144.
147.
141.
129.
139.
142.
167.
147.
185.
207.
171.
120.
131.
138.
140.
146.
168.
137.
154.
147.
138.
130.
166.
152.
135.
119.
141.
157.
118.
149.
244.
179.
182.
183.
80.
29.
SOWS
M/S
.763
.635
.547
.785
.880
1.024
1.096
1.032
.854
.617
.830
.836
.978
.873
.984
1.166
.863
.570
.602
.335
.423
.420
.359
.240
.242
.328
.443
.408
.350
.433
.493
.338
.248
.232
.176
.124
.195
.153
.223
.140
.179
.112
.118
.168
.154
.186
.206
.225
.400
.239
.190
.185
.421
.812
.929
.848
.625
.839
SDWD
DEC
12.5
12.4
9.6
9.4
12.1
9.7
10.5
10.1
10.7
10.5
10.8
11.3
12.4
11.3
11.4
12.9
15.0
32.9
26.0
12.7
6.4
5.2
7.2
12.8
6.2
7.3
8.1
15.3
20.4
15.3
10.6
11.0
7.4
13.8
8.3
7.5
7.8
11.9
9.8
11.3
12.9
10.9
11.3
7.3
13.3
9.2
9.7
8.0
9.4
13.8
23.9
19.1
24.6
16.3
15.1
14.5
14.3
13.2
SDEPA
DEG
14.9
14.4
16.0
10.4
21.7
15.2
20.5
10.7
24.0
13.5
11.7
12.9
14.1
13.4
12.2
14.2
18.5
40.5
28.8
33.1
7.9
6.3
15.5
26.3
9.5
10.5
17.6
29.5
28.8
27.1
37.6
40.1
11.2
42.1
23.3
14.3
12.9
25.7
13.9
16.9
20.6
25.0
36.1
19.0
29.5
20.0
19.2
13.7
13.3
22.0
35.0
89.5
59.1
19.7
17.0
15.9
23.6
13.7
TEMP
°C
9.6
9.8
9.8
9.6
9.9
9.8
8.2
8.6
7.9
7.2
7.6
7.6
7.5
7.5
7.4
7.4
7.1
7.1
7.3
6.2
5.6
4.9
4.7
3.7
4.7
6.4
7.3
8.8
9.4
10.6
10.0
9.8
8.3
5.8
5.7
5.0
4.3
5.0
5.2
4.7
4.6
3.9
3.8
2.9
2.5
1.1
.6
.7
1.3
1.7
2.9
4.9
7.5
9.6
9.4
8.9
6.4
5.5
DTDZ
°C
.08
.47
-.02
-.04
-.15
.08
.08
-.05
.11
.16
.11
.08
.05
.05
.12
.10
.12
.14
.18
.47
.40
.60
.42
.98
.55
-.54
-.44
-.74
-.56
-1.24
-.53
-.33
.32
1.39
1.29
1.43
1.29
.32
.13
.48
.30
.59
.47
.74
.58
.17
-.07
-.18
-.24
-.21
-.63
-.94
-1.33
-2.05
-1.75
-1.31
.36
.68
SOLRAD
W/NT2
20.
62.
45.
61.
143.
40.
67.
71.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
61.
165.
165.
188.
199.
253.
163.
71.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
24.
42.
98.
258.
259.
217.
147.
72.
3.
0.
PCPN
IN
.00
.00
.00
.00
.00
.08
.01
.01 ,
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
79

-------
YEAR DAY HR   WS  WD   SDWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S   PEG   PEG    °C    °C   W/M"2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
198'9
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
344
344
344
344
344
344
345
345
345
345
345
345
345
345
345
345
345
345
345
345
345
345
345
345
345
345
345
345
345
345
346
346
346
346
346
346
346
346
346
346
346
346
346
346
346
346
346
346
346
346
346
346
346
346
347
347
347
347
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
2.7
2.2
2.6
1.8
1.1
1.3
1.8
1.7
.9
1.6
1.4
.9
1.0
1.2
1.5
1.2
1.3
1.0
1.0
1.3
.8
.8
1.2
1.3
1.4
.7
1.6
1.8
.9
1.4
1.8
1.5
1.1
.9
1.3
1.6
1.5
.7
1.5
1.7
1.2
1.1
1.5
1.2
.6
.8
.9
1.1
.5
.9
.7
.7
1.1
.7
1.3
1.2
.6
.7
40.
37.
41.
93.
96.
134.
159.
145.
146.
137.
138.
127.
139.
154.
138.
129.
132.
113.
198.
165.
147.
135.
137.
133.
127.
147.
137.
135.
134.
152.
129.
138.
156.
141.
144.
128.
151.
140.
158.
149.
116.
168.
153.
146.
188.
119.
91.
82.
199.
95.
235.
57.
300.
219.
45.
39.
75.
124.
.665
.604
.688
.560
.397
.282
.371
.270
.178
.196
.197
.159
.107
.167
.188
.266
.254
.240
.309
.287
.230
.242
.251
.152
.237
.182
.198
.328
.141
.236
.243
.215
.153
.135
.171
.231
.261
.185
.250
.360
.287
.260
.347
.322
.226
.306
.275
.318
.194
.339
.345
.300
.356
.206
.457
.476
.190
.175
12.3
11.0
11.8
21.9
23.4
21.5
8.6
8.5
16.9
5.6
7.8
11.2
11.0
5.9
6.2
11.3
11.2
21.2
22.8
13.3
18.1
26.3
15.7
11.1
11.4
19.1
10.0
10.1
14.7
11.5
8.8
7.8
8.1
8.1
10.7
10.3
16.8
19.2
10.9
9.7
18.6
13.3
12.6
20.0
30.3
31.7
30.3
18.1
41.1
26.8
45.9
25.9
19.9
34.0
24.3
25.1
17.2
18.4
18.2
12.0
12.2
62.0
50.2
38.8
14.3
13.1
42.8
10.6
12.0
29.1
22.0
9.8
7.4
16.8
22.2
61.3
48.6
20.1
32.5
38.7
24.3
19.3
19.2
32.1
16.0
19.5
23.4
17.5
14.0
13.1
25.9
30.4
30.0
17.2
25.9
42.0
14.1
12.2
32.6
17.2
15.5
24.8
56.5
86.6
58.9
55.6
81.2
54.3
78.0
48.9
26.8
86.0
38.9
38.4
42.3
33.1
4.8
3.9
3.9
3.7
2.5
1.4
.7
-.3
-.8
-1.1
-1.8
-2.1
-2.3
-2.0
-1.5
-.5
.5
2.1
4.0
4.6
5.3
5.3
2.5
1.6
.6
-.1
-.6
-.6
-1.0
-1.0
-1.6
-2.0
-2.3
-2.1
-2.3
-2.5
-2.3
-2.0
-1.4
-.4
2.6
3.4
4.1
5.1
6.1
5.8
4.5
3.5
4.6
4.6
4.9
4.6
4.9
5.0
5.2
5.1
4.0
3.9
.85
1.04
.90
.75
1.27
.65
.34
.27
.58
.20
-.04
.08
.60
.49
-.03
-.42
-.60
-1.01
-.88
-.76
-.93
-.71
.79
1.16
.79
1.42
.88
.43
.84
.44
.34
.11
.25
.15
.27
.28
.22
.20
-.14
-.56
-1.62
-.64
-.53
-.76
-.67
.06
.87
1.31
.28
.39
.15
.40
.03
.09
.16
.10
.61
.49
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
29.
63.
107.
159.
238.
210.
129.
54.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
36.
148.
305.
269.
161.
191.
127.
34.
5.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
                                      80

-------
YEAR DAY HR   WS  WD
             M/S  PEG
SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
                   °C    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
347
347
347
347
347
347
347
347
347
347
347
347
347
347
347
347
347
347
347
347
348
348
348
348
348
348
348
348
348
348
348
348
348
348
348
348
348
348
348
348
348
348
348
348
349
349
349
349
349
349
349
349
349
349
349
349
349
349
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
.8
.8
1.4
.8
1.5
1.5
1.2
1.1
1.6
2.2
1.8
2.2
1.3
1.1
.9
.7
1.7
.9
1.4
1.5
1.3
1.7
1.8
1.4
1.5
1.4
1.6
1.6
1.9
1.1
1.2
1.4
.8
.9
1.2
1.4
1.2
1.2
.6
1.2
1.2
1.5
1.2
1.4
1.4
1.3
1.7
1.6
1.1
1.4
.8
1.2
1.8
1.2
.9
1.2
1.8
2.0
118.
157.
111.
157.
138.
153.
188.
179.
110.
75.
238.
95.
84.
40.
171.
84.
139.
142.
163.
120.
135.
139.
129.
153.
135.
129.
135.
134.
133.
135.
150.
132.
114.
126.
82.
44.
123.
123.
148.
149.
112.
138.
150.
133.
137.
153.
144.
136.
137.
135.
132.
141.
151.
161.
149.
110.
118.
44.
.248
.309
.214
.220
.205
.259
.282
.251
.580
.648
.594
.559
.268
.141
.213
.260
.246
.224
.345
.260
.238
.249
.272
.215
.222
.244
.300
.235
.307
.150
.190
.229
.170
.209
.468
.425
.171
.149
.170
.159
.212
.430
.350
.288
.252
.194
.375
.242
.283
.360
.173
.200
.224
.231
.223
.393
.490
.659
31.9
34.0
23.7
22.0
8.4
13.2
17.8
13.8
23.8
19.1
27.2
14.9
12.3
8.1
16.7
30.0
14.0
19.4
13.4
16.2
9.1
9.0
7.4
8.9
8.8
9.1
8.5
7.9
8.0
7.8
10.2
9.2
12.9
17.7
36.0
16.9
8.5
6.8
27.5
7.1
16.7
26.3
17.5
10.5
10.5
8.1
8.6
9.0
15.0
21.0
21.2
8.0
5.4
9.4
12.6
33.6
17.1
18.4
	 fc-rj-"8ii 	
60.3
56.6
37.4
33.8
14.2
19.6
30.4
24.1
88.6
27.3
72.7
21.5
44.6
14.2
56.2
68.6
21.5
27.9
24.0
21.2
21.7
19.9
13.5
14.2
11.6
15.5
11.4
14.3
12.0
13.3
15.5
13.1
19.3
26.2
57.6
23.4
22.1
15.5
50.1
17.7
28.5
30.0
30.6
20.8
20.0
13.1
12.8
13.2
21.7
27.9
37.7
20.0
8.3
19.1
16.0
53.5
26.7
21.4
3.3
2.3
.7
.3
0.0
1.7
4.2
5.8
8.4
9.8
9.2
8.7
5.3
2.8
2.7
2.4
1.3
.9
.8
-.4
-.6
-1.1
-1.5
-1.4
-1.6
-1.5
-1.1
-1.0
-1.3
-.3
1.1
2.1
3.3
4.2
5.7
5.3
2.8
2.1
1.6
.8
.1
1.6
1.7
1.0
.3
-.2
-.6
-.4
.1
.5
.8
1.4
1.9
2.8
3.9
5.3
6.4
6.4
.56
.97
.54
.84
.80
.01
-.59
-.80
-1.99
-2.77
-1.74
-1.54
1.26
2.59
1.61
1.36
.85
.86
.54
.69
.90
.25
.01
.20
.03
-.11
-.19
-.16
-.17
-.47
-.58
-.76
-.97
-.53
-.16
.54
1.55
1.72
1.38
1.61
1.31
.33
.08
.24
.74
.41
-.13
-.18
-.06
-.07
-.07
-.03
-.13
-.36
-.43
-.51
-.56
-.48
0.
0.
0.
1.
17.
114.
234.
278.
289.
251.
156.
58.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
38.
63.
88.
91.
74.
52.
43.
28.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
19.
103.
100.
103.
65.
59.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                       81

-------
YEAR DAY HR   WS  WD
             M/S PEG
SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
 M/S   PEG  PEG     °C    °C   W/M^2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
349
349
349
349
349
349
349
349
349
349
350
350
350
350
350
350
350
350
350
350
350
350
350
350
350
350
350
350
350
350
350
350
350
350
351
351
351
351
351
351
351
351
351
351
351
351
351
351
351
351
351
351
351
351
351
351
351
351
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1.9
2.1
2.4
2.3
3.0
1.6
2.3
2.2
1.2
1.8
2.1
1.5
1.4
1.8
1.7
1.3
.8
.8
1.5
1.7
2.2
2.4
1.4
1.8
2.1
1.9
1.8
1.5
1.3
1.0
1.5
2.1
1.3
1.4
1.7
1.1
1.2
1.5
1.6
1.8
1.5
1.2
1.6
1.7
1.6
1.2
.7
1.2
.7
.8
1.0
1.8
1.5
1.6
1.6
.8
.9
1.3
63.
50.
65.
66.
66.
79.
106.
103.
99.
110.
103.
114.
121.
120.
108.
122.
151.
50.
134.
139.
143.
153.
143.
142.
136.
140.
114.
125.
136.
164.
86.
91.
107.
40.
80.
134.
142.
111.
117.
149.
134.
120.
141.
135.
139.
151.
163.
179.
178.
150.
156.
105.
97.
89.
87.
118.
117.
112.
.564
.679
.645
.612
.705
.438
.388
.368
.287
.402
.345
.223
.220
.290
.327
.220
.227
.282
.336
.300
.346
.393
.317
.370
.370
.322
.228
.228
.232
.333
.429
.532
.258
.398
.421
.315
.244
.274
.276
.294
.230
.200
.241
.270
.275
.311
.248
.289
.180
.162
.208
.289
.296
.284
.227
.196
.220
.246
17.3
18.9
15.6
17.1
12.9
18.2
8.6
8.3
12.0
14.1
7.5
8.1
9.4
7.3
10.4
9.5
17.8
20.9
11.0
9.6
9.2
9.3
14.2
11.3
8.7
9.4
8.1
7.9
9.5
34.2
19.5
12.7
9.9
17.9
15.8
20.3
9.8
9.3
9.3
8.6
9.8
9.4
7.5
9.3
8.9
18.0
21.4
13.3
19.1
16.1
13.0
10.8
11.4
8.4
7.9
19.0
18.8
11.6
21.3
22.1
21.4
22.0
15.9
21.1
9.5
9.7
16.7
17.3
9.2
10.3
13.2
12.9
20.3
22.8
45.4
35.3
17.9
12.7
11.2
13.5
22.6
12.3
10.8
11.1
13.3
13.2
13.4
84.7
36.9
17.7
30.4
43.8
26.4
26.6
21.0
14.4
22.4
9.4
13.0
12.4
11.2
12.2
17.2
28.1
31.8
21.6
36.9
40.6
14.6
17.4
17.1
11.1
11.1
38.2
22.5
22.8
5.8
5.6
4.9
4.6
4.3
4.4
4.1
3.9
4.0
4.0
3.8
3.8
3.9
3.7
3.5
3.5
3.5
3.6
3.3
3.1
3.3
3.4
4.0
4.1
4.1
3.9
3.8
3.5
3.4
3.5
3.7
3.2
3.0
3.2
2.6
2.2
2.2
2.3
2.0
1.7
1.8
1.9
1.9
2.4
3.0
3.4
3.9
4.2
4.3
4.5
4.6
4.5
4.3
4.2
4.1
4.0
4.0
3.9
-.37
-.19
-.06
-.10
-.06
-.09
-.12
-.16
-.18
-.17
-.15
-.07
-.11
-.23
-.18
-.13
-.14
-.26
-.24
-.30
-.37
-.27
-.44
-.36
-.39
-.26
-.27
-.25
-.19
-.14
-.26
-.25
-.17
-.26
-.32
-.22
-.17
-.30
-.24
-.14
-.27
-.29
-.21
-.38
-.44
-.43
-.34
-.24
-.23
-.18
-.05
.01
.04
.10
.14
.05
.02
.03
32.
13.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
7.
31.
50.
54.
63.
62.
37.
15.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
8.
39.
68.
89.
91.
74.
36.
9.
1.
0.
0.
0.
0.
0.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      82

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
352
352
352
352
352
352
352
352
352
352
352
352
352
352
352
352
352
352
352
352
352
352
352
352
353
353
353
353
353
353
353
353
353
353
353
353
353
353
353
353
353
353
353
353
353
353
353
353
354
354
354
354
354
354
354
354
354
354
HR
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
WS
M/S
1.7
1.6
1.7
1.5
1.6
1.9
1.8
2.1
2.1
2.1
1.8
1.1
.6
.6
1.7
1.7
2.0
2.6
1.4
1.4
1.7
1.9
1.4
1.6
1.3
1.4
1.7
2.7
2.5
1.7
2.2
2.5
2.2
2.6
2.9
2.9
3.2
4.2
4.4
3.2
2.5
2.8
2.6
2.6
2.7
1.6
1.1
1.4
2.1
2.7
1.2
1.6
3.1
2.9
2.7
1.5
.9
1.6
WD
DP.R
137.
128.
134.
117.
125.
116.
129.
141.
132.
126.
136.
127.
139.
96.
312.
302.
228.
225.
224.
195.
136.
170.
155.
127.
124.
151.
163.
204.
200.
191.
180.
186.
197.
195.
178.
197.
194.
200.
201.
187.
190.
188.
186.
184.
183.
185.
186.
216.
184.
Ill,
183.
209.
212.
192.
151.
112.
129.
143.
SOWS
M/S
.224
.273
.233
.209
.241
.316
.332
.328
.249
.273
.334
.329
.193
.213
.363
.327
.385
.382
.269
.316
.284
.360
.282
.233
.208
.313
.606
.621
.647
.441
.683
.645
.574
.665
.684
.733
.827
1.140
1.188
.932
.731
.676
.613
.657
.653
.344
.292
.429
.474
.538
.322
.420
.656
.670
.468
.259
.220
.315
SDWD
DEC
7.7
9.2
6.2
10.5
7.5
10.5
8.9
8.4
4.8
7.5
10.8
20.0
24.3
26.2
19.7
13.6
10.1
7.7
11.2
12.8
9.2
9.6
11.2
8.4
9.9
12.1
24.5
11.9
12.7
14.6
18.7
13.0
15.0
13.2
12.4
13.5
14.5
12.4
12.8
13.1
15.9
12.8
12.1
12.9
11.2
12.9
13.9
17.5
10.7
10.4
12.0
14.9
10.9
10.6
8.2
9.5
26.3
10.3
SDEPA
DEC
15.5
14.7
10.4
23.6
9.3
17.5
11.4
10.1
5.4
8.4
14.0
26.1
85.3
53.2
28.2
31.2
22.3
17.0
15.4
20.9
15.0
10.7
18.7
11.1
11.9
18.7
48.2
13.2
15.5
18.0
21.0
20.9
16.1
13.6
14.3
16.1
15.1
13.3
13.4
14.6
16.5
13.8
12.5
13.4
17.7
21.8
19.8
38.6
13.3
15.1
14.4
20.6
16.5
12.4
19.5
21.7
33.6
16.3
TEMP
°C
3.7
3.6
3.4
3.3
3.1
3.0
2.8
2.5
2.2
2.9
3.6
4.3
4.8
5.3
5.0
4.8
4.6
4.3
4.0
4.0
4.0
4.3
4.1
3.9
3.9
4.1
4.6
5.1
5.3
5.6
5.8
5.9
5.9
6.2
6.8
7.8
8.4
8.9
8.8
8.7
8.6
8.6
8.5
8.4
8.1
7.9
7.9
8.0
8.2
8.2
8.1
8.1
8.3
8.0
7.8
7.5
7.7
8.5
DTDZ
°C
-.06
-.05
-.06
-.06
-.12
-.01
0.00
-.04
-.15
-.49
-.65
-.71
-.57
-.56
-.28
-.16
-.06
-.10
-.09
-.09
-.10
-.04
-.09
-.13
-.10
-.01
.01
.02
.02
.02
.00
.02
-.06
-.05
-.10
-.14
-.13
-.10
-.05
-.04
.01
.05
.06
.05
.04
.08
.15
.12
.10
.08
.07
.12
.08
.03
.06
.39
.28
-.20
SOLRAD PCPN
W/MA2 IN
0.
0.
0.
0.
0.
0.
0.
1.
18.
83.
151.
122.
86.
72.
72.
10.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
19.
34.
85.
92.
92.
63.
48.
31.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
22.
101.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
83

-------
YEAR DAY HR   WS  WD
             M/S PEG
SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
 M/S   PEG  PEG    °C    °C   W/MA2  IN
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
354
354
354
354
354
354
354
354
354
354
354
354
354
354
355
355
355
355
355
355
355
355
355
355
355
355
355
355
355
355
355
355
355
355
355
355
355
355
356
356
356
356
356
356
356
356
356
356
356
356
356
356
356
356
356
356
356
356
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
1.2
.9
1.1
1.0
1.5
1.6
1.2
.4
.8
1.3
1.3
.9
.7
1.3
.8
1.6
1.7
1.3
1.3
1.2
1.4
1.2
.4
.8
1.7
1.1
.8
1.2
1.4
1.8
1.6
1.2
.8
.9
1.3
1.6
.6
1.5
.9
1.3
2.0
1.4
1.2
1.2
1.8
1.2
2.3
2.6
1.3
1.7
.9
1.1
1.1
1.3
.6
1.2
2.1
1.9
185.
150.
233.
247.
310.
307.
247.
214.
138.
128.
156.
140.
156.
137.
141.
131.
133.
137.
149.
146.
140.
138.
198.
125.
148.
152.
195.
270.
295.
288.
198.
313.
191.
236.
323.
317.
142.
139.
137.
137.
139.
137.
130.
146.
140.
121.
135.
153.
141.
307.
278.
172.
125.
141.
194.
132.
148.
141.
.228
.223
.243
.270
.227
.274
.235
.131
.127
.225
.231
.164
.163
.184
.157
.161
.178
.214
.145
.124
.149
.137
.107
.129
.282
.239
.217
.161
.202
.243
.415
.340
.263
.249
.233
.403
.219
.200
.236
.148
.260
.279
.122
.263
.346
.212
.395
.394
.332
.304
.267
.277
.221
.218
.243
.209
.270
.287
11.4
12.1
24.4
20.4
10.6
10.0
14.4
24.4
11.8
8.8
15.3
23.7
10.0
9.4
16.0
6.1
6.3
8.9
6.3
5.8
5.3
5.2
16.7
7.5
7.5
12.7
17.1
9.0
7.7
7.5
16.2
16.6
27.7
27.6
9.9
19.2
30.1
10.4
18.2
4.5
6.1
8.9
7.1
13.1
9.0
10.5
6.4
6.8
23.4
12.8
20.8
14.7
15.7
9.8
29.0
12.1
7.8
9.9
13.9
26.2
44.0
65.6
17.9
21.1
39.7
68.5
31.3
24.4
21.8
41.4
24.1
21.2
25.9
20.7
10.7
15.8
8.5
8.8
8.8
7.9
55.5
16.7
8.8
18.3
47.0
30.0
17.0
11.8
26.9
27.2
63.2
56.4
13.4
21.2
95.7
20.4
32.9
16.5
12.2
12.2
25.2
24.9
14.0
25.8
10.4
8.1
43.2
31.5
54.6
27.3
30.5
18.6
77.5
28.2
10.2
16.2
8.5
8.7
8.8
9.0
8.8
8.6
8.1
7.6
6.8
7.0
7.4
7.0
6.7
6.3
5.2
4.4
3.7
3.6
3.3
3.1
3.5
3.5
3.9
5.2
5.5
6.9
8.6
9.0
8.8
8.7
8.9
8.6
7.9
7.9
7.4
7.7
6.7
5.3
4.5
3.8
3.4
3.8
4.1
4.2
3.9
3.9
4.2
4.2
4.7
5.2
6.7
7.3
8.1
8.0
7.5
7.5
6.8
5.8
-.20
-.22
-.20
-.27
-.14
-.02
.15
.48
1.01
.60
.20
.25
.39
.29
1.04
1.19
.81
.53
.45
.24
-.02
.05
.21
-.37
-.33
-.53
-.64
-.55
-.25
-.06
-.01
.14
.56
.45
.60
.28
.57
.65
.77
1.15
.51
-.04
.01
-.12
-.15
-.20
-.17
-.21
-.35
-.42
-.72
-.56
-.49
-.08
.31
.64
.88
.67
121.
73.
84.
96.
55.
21.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
24.
57.
88.
173.
213.
148.
82.
33.
4.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
14.
49.
89.
129.
174.
146.
57.
16.
3.
0.
0.
0.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                                      84

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
356
356
356
356
357
357
357
357
357
357
357
357
357
357
357
357
357
357
357
357
357
357
357
357
357
357
357
357
358
358
358
358
358
358
358
358
358
358
358
358
358
358
358
358
358
358
358
358
358
358
358
358
359
359
359
359
359
359
HR
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
WS
M/S
3.3
1.9
1.8
2.3
1.4
.5
.6
1.0
.7
.9
.9
1.2
1.5
.5
.8
.6
1.3
.9
1.9
.7
.4
.7
1.3
1.0
.6
1.1
.9
.6
1.0
1.2
1.3
1.0
1.0
1.9
2.6
1.0
1.0
1.9
.8
2.2
1.9
2.0
.9
1.1
1.0
1.5
1.6
1.5
1.8
.6
.5
1.1
.9
1.4
1.2
1.2
1.8
1.2
WD
DEC
144.
156.
149.
141.
159.
264.
217.
133.
97.
148.
149.
168.
144.
211.
113.
85.
140.
262.
332.
88.
147.
247.
326.
205.
247.
154.
267.
204.
217.
70.
252.
259.
35.
88.
104.
130.
179.
159.
174.
310.
37.
266.
96.
71.
146.
104.
27.
57.
72.
132.
96.
125.
59.
93.
200.
108.
99.
86.
SOWS
M/S
.508
.276
.342
.366
.282
.178
.144
.169
.157
.183
.149
.238
.271
.145
.186
.179
.288
.216
.391
.176
.166
.212
.283
.228
.173
.197
.188
.219
.331
.351
.349
.324
.395
.260
.315
.264
.224
.341
.258
.558
.597
.379
.279
.272
.289
.466
.466
.378
.436
.216
.175
.272
.222
.271
.295
.328
.364
.293
SDWD
DEC
9.5
9.2
10.0
6.9
14.5
22.5
15.6
8.3
11.8
14.7
16.2
11.3
9.1
17.1
13.3
21.4
13.2
20.3
11.3
22.7
32.0
24.8
11.8
15.3
18.5
13.2
19.5
26.4
31.7
21.9
14.1
22.7
20.1
11.7
7.3
27.3
15.0
9.9
26.5
21.5
19.6
12.1
24.1
18.9
19.7
19.7
16.5
16.1
13.5
26.5
21.9
14.7
16.4
10.1
25.4
14.6
10.9
20.8
SDEPA
DEG
14.0
25.4
12.8
10.8
30.4
54.2
39.8
23.0
55.9
44.5
40.5
18.2
12.2
43.6
38.9
35.9
25.3
73.0
20.1
84.6
88.5
77.1
19.3
99.2
77.8
20.3
67.8
68.3
52.5
50.9
22.5
35.9
34.1
28.5
11.9
53.0
35.5
15.3
52.5
27.6
30.4
14.4
33.3
29.3
46.6
26.3
23.0
20.5
29.3
54.6
45.5
21.1
28.9
20.8
90.6
33.3
20.1
31.4
TEMP
°C
6.7
6.5
7.1
6.4
6.4
6.5
6.7
6.7
6.8
6.9
7.0
7.1
7.2
7.7
8.6
10.0
11.0
12.4
11.8
11.8
11.1
10.3
10.6
10.4
10.0
9.6
9.5
9.4
10.1
9.8
9.7
9.8
9.6
8.5
8.1
8.1
8.0
7.6
8.1
8.6
8.6
8.7
8.6
8.3
8.1
8.1
7.9
7.7
7.4
7.2
7.1
7.1
6.9
6.7
6.4
6.4
6.1
6.0
DTDZ
°C
.24
.31
.20
-.05
-.04
-.02
.01
-.08
-.03
-.04
-.07
-.03
-.10
-.12
-.41
--76
-.43
-.78
-.35
-.23
.25
.58
.32
.28
.25
.22
.09
.42
.15
.11
-.07
-.05
.09
.36
.01
-.13
-.08
-.13
-.18
-.32
-.54
-.59
-.57
-.36
-.24
-.17
-.21
-.14
-.21
-.18
-.21
-.25
-.24
-.29
-.21
-.27
-.25
-.22
SOLRAD
W/MA2
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
7.
30.
53.
130.
157.
183.
72.
39.
4.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
6.
25.
43.
42.
55.
54.
26.
8.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
PCPN
IN
.00
.00
.00
.03
.01
.03
.01
.01
.00
.00
.00
.00
.00
.01
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
85

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
DAY
359
359
359
359
359
359
359
359
359
359
359
359
359
359
359
359
359
359
360
360
360
360
360
360
360
360
360
360
360
360
360
360
360
360
360
360
360
360
360
360
360
360
361
361
361
361
361
361
361
361
361
361
361
361
361
361
361
361
HR
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
WS
M/5
.7
1.9
3.0
1.9
1.8
2.5
.9
.6
.9
1.7
1.5
.9
1.7
1.8
.5
1.2
1.7
1.6
2.8
1.4
1.6
2.4
2.1
2.2
2.5
2.1
2.6
2.5
2.3
1.9
1.7
1.1
1.1
2.0
2.4
2.3
2.7
2.7
2.7
2.7
3.2
3.1
.7
1.1
1.4
2.2
3.2
1.8
2.1
1.8
1.4
.7
.7
1.3
1.6
2.0
1.8
1.2
WD
DEG
189.
147.
144.
165.
148.
152.
168.
79.
111.
118.
96.
140.
156.
120.
161.
94.
146.
159.
153.
151.
144.
151.
146.
144.
149.
161.
140.
146.
146.
147.
143.
160.
148.
141.
141.
143.
149.
141.
137.
137.
130.
133.
116.
171.
120.
132.
144.
144.
139.
143.
166.
115.
124.
140.
140.
137.
137.
124.
SOWS
M/S
.317
.352
.454
.313
.278
.375
.287
.221
.287
.293
.284
.287
.289
.425
.179
.373
.344
.345
.442
.311
.294
.429
.396
.338
.378
.315
.421
.403
.418
.335
.373
.308
.274
.389
.434
.352
.408
.407
.393
.435
.489
.481
.263
.346
.263
.370
.469
.320
.355
.261
.354
.185
.226
.219
.244
.288
.306
.213
SDWD
DEG
27.0
8.9
6.7
8.3
8.2
8.3
20.0
22.3
18.6
11.4
11.0
26.6
8.6
15.7
27.5
25.2
10.5
11.5
7.6
17.6
7.6
6.9
8.3
6.4
6.8
8.8
7.0
8.3
9.3
8.6
16.1
18.7
18.5
8.3
6.9
7.0
7.4
6.3
6.4
6.9
7.0
7.6
28.1
25.5
10.5
7.9
6.5
11.5
9.1
8.8
14.5
17.2
13.5
7.7
7.2
8.0
6.4
9.5
SDEPA
DEG
59.2
10.6
9.8
11.9
9.9
10.4
70.2
42.0
49.1
13.8
22.4
79.6
18.9
27.0
61.6
48.2
12.4
18.9
8.4
34.1
11.8
7.6
9.8
9.6
7.4
13.4
7.6
9.0
10.5
9.6
19.5
29.9
26.6
8.9
8.3
8.0
7.9
7.9
7.4
7.2
7.7
11.3
52.9
50.6
16.9
10.3
9.1
21.1
16.2
12.9
30.1
35.9
19.1
13.9
9.8
10.8
9.0
11.6
TEMP
°C
5.9
5.5
5.1
5.1
5.3
5.4
5.6
6.4
6.3
5.8
5.3
5.1
4.9
4.8
4.7
5.0
4.3
4.2
3.8
3.8
3.8
3.3
3.2
3.1
3.1
2.9
2.7
3.0
2.9
3.2
3.4
3.5
3.8
3.6
3.4
3.2
2.8
2.4
2.3
2.2
1.8
1.3
1.0
.7
.6
0.0
-.6
-.5
-.3
-.3
.1
.9
2.6
3.3
4.0
4.8
5.3
5.4
DTDZ SOLRAD
°C W/M-2
-.15
-.18
-.20
-.17
-.30
-.30
-.42
-.76
-.52
-.45
-.43
-.27
-.16
-.25
-.18
-.23
-.20
-.16
-.14
-.17
-.18
-.15
-.16
-.15
-.14
-.13
-.21
-.25
-.29
-.31
-.32
-.29
-.29
-.30
-.22
-.20
-.19
-.20
-.18
-.19
-.26
-.22
-.26
-.22
-.39
-.30
-.03
.02
.11
.11
-.08
-.51
-.76
-.46
-.49
-.47
-.20
-.16
0.
0.
6.
23.
35.
59.
66.
37.
20.
7.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
16.
34.
54.
68.
62.
64.
32.
12.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
27.
79.
97.
33.
69.
54.
18.
6.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.04
86

-------
SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
                    °C    °C
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
361
361
361
361
361
361
361
361
362
362
362
362
362
362
362
362
362
362
362
362
362
362
362
362
362
362
362
362
362
362
362
362
363
363
363
363
363
363
363
363
363
363
363
363
363
363
363
363
363
363
363
363
363
363
363
363
364
364
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
.6
1.1
1.1
1.1
1.3
1.1
1.0
1.0
1.0
1.0
.9
.5
.6
.8
1.2
.9
.7
.8
1.5
1.4
1.9
2.2
1.6
.8
1.0
1.2
.4
.7
1.6
1.3
1.3
1.0
1.2
1.3
1.4
2.0
1.8
.8
.9
1.5
1.5
1.7
.9
1.8
2.2
2.2
2.2
2.1
1.8
2.3
1.7
1.4
.8
1.5
1.5
.9
.6
.7
179.
154.
184.
140.
238.
200.
133.
170.
133.
153.
127.
123.
91.
174.
133.
148.
138.
259.
338.
44.
338.
331.
316.
170.
89.
154.
147.
140.
141.
137.
142.
153.
125.
129.
139.
151.
142.
156.
177.
113.
123.
127.
181.
192.
199.
179.
188.
182.
173.
181.
173.
164.
155.
154.
144.
121.
103.
272.
.201
.238
.239
.194
.239
.182
.181
.183
.130
.162
.171
.147
.167
.158
.194
.181
.166
.179
.345
.414
.470
.483
.342
.168
.153
.217
.105
.186
.276
.211
.195
.191
.205
.232
.228
.365
.247
.210
.182
.180
.212
.250
.278
.464
.472
.561
.533
.531
.442
.506
.354
.308
.272
.301
.291
.115
.174
.157
20.2
17.5
16.3
12.7
14.3
11.0
13.0
13.2
8.4
9.2
10.8
15.1
11.9
12.4
9.5
18.7
16.0
16.8
13.1
15.7
12.3
12.4
11.6
13.4
5.9
12.3
19.7
13.2
10.1
10.1
9.3
16.4
11.1
12.1
11.9
9.3
11.4
18.0
21.6
10.3
8.1
9.2
18.9
17.5
11.4
16.3
13.7
12.8
11.3
11.2
12.9
13.8
26.4
15.8
8.8
11.2
20.5
18.5
— ivj-jvj
59.7
25.7
73.0
24.2
23.5
37.8
26.6
34.1
15.1
20.5
20.1
65.3
54.1
32.8
12.4
48.0
68.2
51.0
16.9
22.4
14.8
17.0
17.6
37.2
13.8
56.3
57.8
65.7
17.5
18.8
26.6
23.9
29.0
20.1
17.9
13.0
21.9
35.9
46.0
14.1
16.4
18.0
32.7
23.4
15.2
20.3
20.1
13.5
14.5
16.8
17.2
19.6
61.3
20.4
20.6
16.0
59.7
34.0
5.4
5.4
5.1
5.2
5.5
5.6
5.5
5.4
5.5
5.5
5.3
5.4
5.4
5.5
5.4
5.3
4.8
6.1
7.0
7.2
7.5
7.6
7.5
7.3
6.6
6.4
5.6
4.4
4.4
3.8
3.7
3.3
3.3
3.4
3.5
3.6
3.4
3.6
3.8
3.4
3.3
5.1
6.0
7.7
8.0
8.7
8.8
8.6
8.5
8.1
7.6
7.5
7.5
7.8
7.6
7.2
6.7
7.3
.05
-.04
-.06
.02
.10
.02
-.10
-.01
.01
.07
.09
.07
.07
.03
-.05
.08
.69
.11
-.08
-.19
-.25
-.21
-.14
.04
.51
.41
.74
1.24
.39
.53
.59
.35
.12
.01
.09
-.01
0.00
.05
.09
.17
.50
-.41
-.31
-.62
-.37
-.28
-.10
-.03
-.02
0.00
-.02
-.02
.14
.11
.24
.72
1.11
.25
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
34.
56.
45.
68.
78.
65.
48.
16.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
21.
120.
136.
271.
184.
131.
28.
11.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
— ±±> 	
.08
.07
.01
.01
.00
.00
.00
.00
.00
.00
.00
.01
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
                87

-------
YEAR
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1989
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
DAY
364
364
364
364
364
364
364
364
364
364
364
364
364
364
364
364
364
364
364
364
364
364
365
365
365
365
365
365
365
365
365
365
365
365
365
365
365
365
365
365
365
365
365
365
365
365
1
1
1
1
1
1
1
1
1
1
1
1
HR
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
1
8
9
10
11
12
WS
M/S
.8
.3
.3
.7
1.0
.9
1.3
1.0
.4
.5
1.3
1.5
1.5
1.2
1.0
.7
.9
.9
1.1
.7
1.4
1.4
1.6
1.2
2.6
2.4
1.6
2.3
3.5
3.5
3.1
2.4
2.6
3.3
3.6
6.1
4.0
3.4
3.3
4.1
3.3
3.4
3.3
4.3
3.8
3.0
2.8
4.0
4.4
3.0
3.6
3.6
3.4
2.7
2.8
3.9
4.0
4.6
WD
DEC
183.
177.
170.
168.
133.
144.
138.
140.
159.
166.
45.
137.
182.
80.
114.
57.
36.
55.
101.
99.
174.
226.
191.
163.
138.
142.
155.
156.
127.
121.
125.
118.
153.
159.
185.
202.
197.
194.
178.
174.
181.
176.
179.
177.
171.
161.
176.
197.
207.
195.
192.
195.
188.
186.
173.
186.
204.
221.
SDWS
M/S
.128
.106
.119
.129
.134
.148
.227
.205
.121
.213
.352
.389
.410
.367
.341
.196
.253
.265
.220
.198
.242
.346
.315
.288
.474
.441
.426
.502
.600
.563
.573
.406
.625
.740
.835
1.450
.923
.818
.755
.894
.811
.757
.756
.937
.886
.582
.720
.957
1.001
.704
.860
.902
.810
.695
.702
.955
1.029
1.116
SDWD
DEC
12.2
24.8
25.2
13.0
5.9
10.0
10.3
10.7
26.6
33.7
14.1
17.1
19.0
13.9
22.9
13.5
15.7
13.6
11.3
13.9
11.1
13.8
12.3
14.4
7.9
7.6
16.3
14.8
8.5
7.4
8.9
11.4
13.1
12.0
12.1
11.2
12.7
11.8
11.9
10.2
12.3
11.2
11.6
10.8
10.2
9.9
11.8
11.1
10.7
11.8
11.6
11.8
12.1
13.8
12.2
12.5
13.0
12.8
SDEPA
DEC
60.6
99.7
87.3
44.9
15.6
13.6
21.4
23.8
71.2
93.9
16.3
33.2
32.0
39.9
38.4
19.6
22.3
22.8
30.2
27.7
21.3
38.7
27.8
28.4
9.1
8.8
30.1
22.6
9.5
8.7
13.1
13.2
19.0
15.1
13.2
12.3
17.2
15.5
12.3
10.5
15.4
12.8
12.4
11.2
10.6
11.7
19.3
11.8
11.6
12.3
12.7
12.5
14.6
14.5
16.8
14.5
17.3
15.0
TEMP
°C
7.0
6.4
6.6
6.5
6.4
6.4
6.7
7.1
7.8
8.5
9.2
9.1
8.9
8.8
8.3
7.6
7.0
6.9
7.0
6.8
6.7
6.8
6.4
6.2
5.7
4.9
4.8
4.7
4.5
4.6
4.7
6.0
8.4
9.9
10.0
9.0
8.5
8.8
8.8
8.7
8.2
7.9
7.8
8.1
8.0
7.8
7.8
7.5
7.3
6.8
6.6
6.6
6.4
6.0
5.9
6.0
6.3
7.0
DTDZ
°C
.26
.42
.33
.26
.14
.05
-.13
-.21
-.36
-.41
-.77
-.59
-.42
-.26
0.00
.54
.77
.58
-.06
-.15
-.09
-.07
-.12
-.13
-.19
-.18
-.01
.18
.10
-.01
.10
.15
-.25
-.44
-.09
-.04
-.05
.03
.11
.10
.09
.07
.11
.11
.09
.13
.12
.08
.19
.04
.04
.03
.02
.04
0.00
-.01
-.05
-.35
SOLRAD
W/M^2
0.
0.
0.
0.
0.
0.
11.
28.
61.
64.
87.
62.
48.
17.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
41.
196.
246.
105.
77.
90.
49.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
18.
58.
84.
258.
PCPN
IN
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.03
.06
.00
.00
.00
.00
.00
.01
.02
.01
.01
.02
.03
.02
.00
.00
.00
.00
.03
.03
.00
.00
.00
.00
.00
.00
.00
.00
.00

-------
YEAR DAY
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1
1
1
1
1
1
1
1
1
1
1
1
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
HR
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
WS
M/S
3.9
5.0
4.9
5.7
5.0
3.7
3.5
3.6
2.2
2.4
2.6
2.3
1.7
2.3
2.0
1.5
1.4
1.5
1.5
1.0
1.3
1.5
.8
.8
1.6
1.5
1.8
2.1
2.3
1.5
1.7
1.6
1.2
1.2
1.8
1.4
1.0
1.5
1.6
1.7
1.9
2.9
2.6
2.6
3.4
3.5
4.2
4.5
5.1
5.2
4.7
4.3
3.3
3.1
3.2
2.4
2.9
1.7
WD
DEG
220.
231.
232.
227.
234.
217.
151.
207.
169.
162.
242.
234.
157.
137.
135.
129.
129.
132.
120.
118.
131.
146.
143.
160.
168.
160.
146.
185.
196.
158.
134.
130.
126.
125.
126.
111.
118.
180.
172.
145.
124.
129.
132.
138.
153.
156.
163.
168.
194.
202.
199.
194.
195.
192.
197.
170.
156.
170.
SOWS
M/S
1.054
1.002
.993
1.219
1.029
.826
.675
.952
.671
.670
.594
.441
.379
.364
.233
.233
.218
.202
.265
.247
.202
.305
.283
.306
.375
.422
.398
.555
.495
.244
.280
.295
.200
.258
.440
.313
.256
.519
.466
.408
.372
.518
.397
.505
.727
.812
1.068
1.078
1.424
1.413
.979
1.054
.954
.886
.834
.574
.653
.540
SDWD SDEPA
DEG DEG
17.4
11.3
10.0
10.0
10.9
12.9
10.2
14.8
19.2
16.5
19.9
12.5
10.3
6.9
6.3
9.0
7.5
6.8
17.2
32.8
9.0
9.9
18.0
25.3
16.1
13.5
12.5
15.0
10.5
7.5
7.5
8.6
9.3
13.9
12.4
13.7
17.1
16.1
14.6
15.6
14.8
7.8
6.4
9.3
9.6
10.0
12.3
11.2
13.0
12.3
11.1
12.6
14.3
14.0
13.7
11.8
10.7
15.4
21.0
14.3
14.6
10.3
12.0
20.4
21.9
24.1
56.0
41.5
42.1
49.1
25.5
12.8
14.3
18.7
13.8
10.0
33.4
52.3
14.4
18.4
30.5
35.1
20.3
22.5
16.8
26.0
11.2
21.2
9.9
12.9
10.8
22.2
15.6
20.5
20.9
23.6
29.9
40.8
35.3
9.4
7.6
13.7
10.4
10.3
14.4
12.1
19.0
12.9
11.8
15.1
15.5
14.6
14.6
14.8
12.0
18.8
TEMP
°C
7.4
8.1
7.5
6.6
5.9
5.0
4.0
4.2
3.7
4.1
4.0
3.8
2.3
1.5
1.4
1.4
1.3
1.1
.7
.7
.4
3.0
5.2
6.9
7.5
7.4
8.0
7.6
6.6
5.4
5.1
5.5
5.4
5.2
5.5
5.3
5.3
5.9
6.1
5.3
5.4
5.3
5.4
6.1
6.8
7.2
7.9
8.5
8.6
8.6
7.6
7.4
7.5
7.5
7.4
7.3
7.1
7.3
DTDZ
°C
-.36
-.55
-.24
-.14
-.01
.04
.22
.15
.25
.08
.10
.08
.67
.93
.48
.41
.85
1.15
1.42
1.33
.85
-.59
-.97
-1.18
-.87
-.63
-.83
-.19
.12
.44
.25
.24
.25
.45
.21
.41
.47
.14
.11
.37
.25
.23
.15
.22
.04
.05
-.01
.04
.14
.11
.04
.01
.03
.01
.01
-.01
.01
.04
SOLRAD
W/MA2
241.
298.
107.
77.
8.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
45.
161.
260.
290.
327.
191.
189.
76.
4.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
5.
32.
41.
37.
25.
46.
23.
7.
1.
0.
0.
0.
0.
0.
PCPN
IN
.00
.00
.00
.00
..00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.01
.00
.01
.01
.03
.01
.00
.00
.00
.00
.00
.00
89

-------
YEAR DAY HR   WS  WD   SDWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG    M/S   PEG  PEG    °C    °C   W/M"2  IN.
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
3
3
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
6
6
6
6
6
6
6
6
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
2.0
2.0
1.7
2.1
2.4
2.8
2.8
3.9
2.4
1.9
2.4
3.3
4.4
5.0
3.5
3.2
3.5
4.7
4.6
2.5
1.6
1.6
2.7
1.7
1.4
2.5
2.4
2.8
1.1
.8
2.2
1.3
1.8
.6
1.3
1.8
2.8
4.9
5.5
6.0
5.3
5.0
4.0
6.0
4.5
4.4
2.9
2.9
3.6
4.8
3.0
4.0
2.7
2.5
2.3
1.6
1.5
1.3
161.
170.
144.
163.
183.
183.
165.
141.
150.
228.
146.
193.
195.
204.
217.
224.
251.
232.
217.
245.
262.
262.
283.
261.
189.
138.
142.
141.
115.
238.
103.
169.
232.
166.
135.
136.
146.
171.
183.
187.
191.
189.
188.
254.
225.
200.
191.
183.
187.
185.
173.
181.
138.
132.
125.
149.
129.
124.
.491
.483
.397
.460
.674
.716
.714
.676
.461
.423
.703
1.042
1.351
1.464
.836
.754
.819
.830
1.212
.892
.524
.380
.449
.330
.302
.348
.423
.426
.228
.219
.378
.285
.342
.235
.274
.257
.512
1.062
1.349
1.515
1.309
1.283
1.007
1.236
.839
1.005
.831
.767
.968
1.136
.820
1.010
.396
.355
.370
.214
.234
.199
14.4
12.8
11.3
11.4
12.9
13.2
13.0
8.9
16.0
15.0
17.4
16.3
16.1
13.5
15.1
13.2
13.4
9.6
13.1
27.9
18.8
13.4
8.5
9.2
20.2
6.7
7.8
7.4
18.4
25.1
11.6
16.6
10.9
28.4
20.1
7.0
9.3
10.5
12.9
12.3
12.9
12.4
13.1
11.1
9.3
10.7
15.1
13.5
12.6
11.8
14.5
13.2
7.6
6.5
7.7
6.3
8.6
9.4
26.2
14.3
19.8
25.8
13.5
14.4
13.7
13.0
36.7
43.4
34.9
17.9
17.4
15.8
18.7
16.5
15.5
11.5
14.3
38.7
27.9
17.9
11.5
24.3
40.2
8.1
11.3
8.7
38.8
58.7
21.9
42.6
58.6
72.6
25.7
11.4
19.7
11.6
13.8
14.7
13.6
14.4
14.2
20.1
12.3
11.7
15.7
14.6
13.4
13.7
20.9
20.8
12.6
13.9
8.2
15.2
10.4
13.3
7.3
7.3
7.2
7.6
8.0
8.1
7.9
7.5
7.4
7.4
8.0
9.6
10.6
11.0
10.9
10.9
11.1
11.1
10.9
10.4
10.0
9.8
9.5
9.4
9.1
8.4
8.5
8.6
8.4
8.9
9.4
8.8
8.4
8.3
8.3
8.6
10.6
12.7
13.4
13.7
12.9
12.2
11.6
10.6
10.6
10.2
10.0
10.0
9.8
9.4
8.4
8.3
7.5
6.9
7.5
7.2
5.7
5.3
.02
.02
.09
.14
.09
.09
.11
.15
.22
.06
.13
.01
-.12
-.08
-.01
.01
.03
.14
.13
.13
.11
.13
.13
.14
.03
-.01
.03
.12
.46
.28
.56
.27
.06
.07
-.04
.27
.20
.12
.07
.06
.14
.14
.16
.38
.22
.13
.08
.08
.10
.07
.19
.13
.50
.93
.79
.68
1.45
2.02
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
19.
69.
154.
118.
24.
22.
46.
30.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
5.
2.
14.
49.
43.
32.
59.
29.
10.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
.00
.01
.00
.03
.03
.06
.08
.05
.00
.01
.00
.00
.00
.01
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.08
.05
.09
.01
.00
.00
.00
.00
.03
.06
.10
.13
.00
.00
.00
.00
.00
.00
.04
.06
.01
.00
.00
.00
.00
.00
                                      90

-------
YEAR DAY HR   WS  WD   SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
             M/S PEG     M/S    PEG  PEG    °C
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
6
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
1.6
1.8
1.2
1.3
2.0
1.1
1.1
1.3
.5
1.0
4.4
5.3
4.7
4.9
5.1
6.5
7.6
6.9
5.5
4.7
4.5
7.3
4.8
2.1
3.7
5.9
6.1
5.9
5.8
3.5
4.8
4.2
3.1
1.9
2.8
2.2
1.6
2.1
1.9
3.6
5.2
5.8
5.3
5.2
3.6
5.4
6.8
3.9
3.6
2.7
2.5
1.6
1.9
2.5
1.5
.9
1.2
1.4
120.
130.
129.
167.
198.
194.
125.
204.
237.
147.
130.
136.
149.
143.
168.
190.
224.
250.
227.
213.
210.
247.
225.
166.
195.
207.
203.
206.
213.
191.
179.
184.
189.
173.
150.
148.
99.
70.
106.
44.
12.
201.
317.
235.
175.
217.
230.
219.
168.
186.
180.
153.
146.
155.
159.
78.
112.
147.
.296
.265
.280
.321
.480
.328
.334
.276
.245
.292
.697
.919
.946
1.031
1.104
1.549
1.706
1.355
1.144
1.101
1.122
1.507
.893
.409
.816
1.149
1.351
1.196
1.211
.862
1.161
1.075
.797
.481
.525
.447
.349
.549
.697
1.120
1.353
1.757
1.074
1.000
.739
1.368
1.345
.897
.779
.741
.579
.409
.386
.547
.276
.165
.219
.342
	 ^•L-"-<
7.7
8.6
17.0
24.4
12.0
15.5
26.0
20.7
36.5
21.4
7.2
8.1
9.2
9.1
10.8
11.8
11.1
9.1
9.6
10.5
11.2
13.1
9.7
11.6
10.6
9.9
10.7
10.4
9.9
11.6
11.3
11.9
11.1
15.9
8.3
10.4
15.3
12.4
21.2
23.2
13.7
14.7
11.8
9.0
11.1
15.6
9.2
11.7
11.6
15.5
12.8
12.6
10.5
11.4
12.7
9.5
20.5
15.7
15.2
10.1
21.2
40.4
15.8
37.0
61.9
96.9
66.5
27.3
7.6
8.5
12.1
9.2
15.0
17.8
27.0
10.8
15.2
12.6
25.5
20.0
10.4
24.2
13.0
10.4
11.1
10.5
15.8
13.0
12.0
15.7
17.0
23.7
9.8
13.4
52.5
30.2
33.3
24.6
14.0
22.1
23.9
20.6
26.5
26.8
9.7
21.0
16.2
17.0
17.8
20.8
20.6
31.5
34.6
18.9
37.0
22.1
6.7
8.8
10.9
11.7
11.4
10.7
10.3
9.1
8.4
8.7
10.6
10.8
10.9
11.2
12.0
12.6
12.0
11.5
11.1
10.8
10.0
9.3
8.6
8.5
9.2
10.0
11.0
11.3
10.4
11.0
11.9
11.8
10.6
9.0
8.4
7.7
7.2
7.2
7.2
7.1
6.9
7.0
6.8
6.8
7.5
8.7
9.0
9.1
8.4
8.9
8.9
8.6
-999.
9.5
9.5
9.1
9.0
8.8
1.18
-.28
-.66
-.41
.00
-.11
0.00
.10
.02
.23
.38
.41
.43
.47
.33
.18
.28
.20
.19
.20
.23
.26
.14
.32
.15
.11
-.02
.06
.12
.06
.05
.09
.17
.09
.04
.19
.19
.27
.13
.09
.11
.23
.81
.61
.14
.19
.14
.11
.03
-.04
-.05
-.18
-999.
.07
-.04
.47
.43
.31
• «/ IM fa
52.
157.
227 .
167.
93.
69.
20.
6.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
25.
80.
172.
104.
81.
109.
52.
14.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
12.
35.
50.
64.
64.
52.
53.
23.
3.
0.
-t^j-" 	
.00
.00
.00
.00
.00
.00
.00
.07
.04
.04
.05
.07
.12
.08
.09
.08
.10
.00
.00
.00
.18
.16
.03
.01
.00
.02
.00
.00
.02
.00
.00
.00
.02
.06
.03
.03
.03
.01
.10
.04
.05
.11
.11
.04
.00
.00
.00
.00
.00
.00
.02
.02
.00
.00
.00
.00
.00
.00
                                       91

-------
YEAR DAY HR   WS  WD
             M/S DEG
SOWS  SDWD SDEPA  TEMP  DTDZ SOLRAD PCPN
 M/S   DEG  DEG    °C    °C   W/M"2  IN
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
1990
8
8
8
8
8
8
9
9
9
9
9
9
9
9
9
9
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
1.2
1.4
1.0
.5
.7
1.4
2.1
1.3
1.5
.7
.9
1.5
1.8
1.9
2.0
2.6
129.
75.
136.
267.
170.
141.
135.
109.
131.
159.
102.
128.
141.
135.
154.
197.
.316
.381
.327
.212
.260
.288
.317
.207
.270
.324
.184
.186
.188
.281
.374
.690
27.5
18.1
29.7
24.0
27.0
20.2
7.4
9.2
9.8
34.5
18.3
14.6
6.0
6.8
10.1
14.1
65.8
26.1
69.0
43.3
65.9
27.3
11.4
12.9
16.4
46.9
21.9
24.0
8.2
12.7
16.7
20.1
8.4
8.0
7.7
7.5
7.4
7.4
7.3
8.2
9.8
10.3
10.4
10.6
10.6
11.0
11.7
12.0
.21
.33
.13
.02
-.06
-.10
-.04
.34
.29
.29
.39
.21
.12
.21
.25
.29
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
5.
.02
.07
.06
.05
.05
.09
.15
.15
.15
.20
.32
.39
.27
.30
.24
.20
                                       92

-------
Appendix B-2. 24-Hourly Meteorological Data
                                        93

-------
Mo/Da
8/21
8/22
8/23
8/24
8/25
8/26
8/27
8/28
8/29
8/30
8/31
9/ 1
9/ 2
9/ 3
9/ 4
9/ 5
9/ 6
9/ 7
9/ 8
9/ 9
9/10
9/11
9/12
9/13
9/14
9/15
9/16
9/17
9/18
9/19
9/20
9/21
9/22
9/23
9/24
9/25
9/26
9/27
9/28
9/29
9/30
10/ 1
10/ 2
10/ 3
10/ 4
U Theta
m/s deg
3.08
1.33
2.05
0.33
0.99
1.17
1.37
1.14
1.34
3.23
0.86
1.08
1.12
1.05
1.29
1.09
1.38
0.67
2.07
3.33
1.11
0.74
0.80
0.73
0.97
1.45
1.57
1.95
0.27
0.80
0.49
0.78
0.89
0.82
0.66
1.82
0.45
1.61
1.00
1.26
2.86
1.01
1.93
0.38
0.70
206
284
277
252
298
333
276
278
345
237
270
205
199
326
304
331
6
336
11
19
356
346
267
297
276
286
158
352
221
1
7
344
266
287
296
221
223
9
13
246
236
6
14
194
157
SO
w/mA2
121.8
213.9
204.2
148.2
247.4
266.0
203.6
172.6
213.2
99.6
107.9
90.7
146.6
251.7
238.1
219.6
246.8
246.7
240.5
256.0
245.8
240.6
227.0
226.8
225.5
230.4
87.4
216.1
221.4
215.8
213.2
210.0
208.5
201.0
204.7
39.3
51.4
132.1
160.9
118.0
140.9
134.9
193.3
186.1
58.6
PPT
in
0.26
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.02
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.12
0.09
0.00
0.00
0.00
0.02
0.00
0.00
0.00
0.03
n
%
0
10
2
4
17
35
3
12
43
0
13
6
7
28
17
31
40
26
38
47
31
23
3
13
2
8
0
58
7
34
27
22
1
12
15
2
2
48
44
3
0
26
45
5
1
ne
%
0
1
1
1
6
2
0
6
14
0
0
1
10
3
0
6
8
1
13
34
5
1
1
1
1
1
0
5
1
2
2
1
1
3
1
2
3
20
9
2
0
16
23
1
1
e
%
0
1
1
10
5
3
3
1
6
0
0
1
5
9
2
3
6
2
3
5
3
4
3
2
6
2
6
1
4
3
3
4
6
2
5
3
11
6
3
6
0
2
2
7
8
se
%
8
11
1
33
21
12
14
11
3
3
17
7
5
15
20
9
23
32
19
6
31
28
32
30
20
13
52
7
47
34
35
28
27
24
26
13
24
10
24
23
0
16
19
39
50
s
%
55
7
1
10
4
10
10
12
3
8
10
34
43
9
7
7
10
11
13
2
9
12
7
10
15
10
24
5
3
5
10
10
11
8
9
23
11
3
12
10
17
22
5
10
15
sw
%
26
13
13
1
1
3
15
6
1
58
13
23
13
3
1
18
3
6
4
1
1
5
4
2
2
17
11
6
3
5
3
3
4
6
4
38
17
1
3
14
36
0
1
10
2
w
%
8
25
50
17
38
18
22
42
15
31
22
14
9
15
35
7
3
17
7
1
16
16
35
23
38
24
6
11
20
11
9
13
39
28
26
13
25
5
1
37
41
10
2
18
15
nw 
-------
Mo/Da
10/ 5
10/ 6
10/ 7
10/ 8
10/ 9
10/10
10/11
10/12
10/13
10/14
10/15
10/16
10/17
10/18
10/19
10/20
10/21
10/22
10/23
10/24
10/25
10/26
10/27
10/28
10/29
10/30
10/31
ll/ 1
ll/ 2
ll/ 3
ll/ 4
ll/ 5
ll/ 6
ll/ 7
ll/ 8
ll/ 9
11/10
11/11
11/12
11/13
11/14
11/15
11/16
11/17
11/18
11/19
11/20
U Theta
m/s deg
0.72
0.58
0.22
0.66
0.39
1.09
3.65
1.66
1.76
1.14
0.36
0.47
0.46
1.39
0.53
2.08
3.01
1.55
1.51
0.35
2.23
2.46
0.26
0.34
0.52
0.96
1.45
0.50
0.65
4.06
2.89
2.47
4.78
2.11
3.94
3.93
0.90
1.45
0.91
2.88
1.04
0.40
0.22
0.49
0.34
1.06
1.04
310
325
230
272
252
151
188
185
204
23
82
216
249
148
195
185
156
154
192
179
170
154
255
65
123
107
18
121
146
190
209
208
202
193
193
191
199
9
99
180
128
28
118
21
163
152
186
So
w/mA2
114.6
89.2
52.1
121.2
128.1
54.3
59.3
33.2
92.6
121.1
146.3
135.0
143.0
48.7
96.7
69.4
49.6
28.8
14.5
67.1
73.8
37.3
91.5
118.1
85.4
47.3
91.1
102.8
46.9
24.2
76.1
60.8
34.3
57.6
27.0
57.0
18.9
20.0
53.2
54.2
89.8
62.4
11.5
18.7
64.6
13.7
35.8
PPT
in
0.01
0.00
0.00
0.00
0.00
0.08
0.02
0.14
0.11
0.00
0.00
0.00
0.00
0.08
0.00
0.18
0.11
0.40
0.41
0.00
0.05
0.40
0.01
0.04
0.00
0.00
0.00
0.00
0.00
0.21
0.09
0.00
0.18
0.01
0.26
0.29
0.56
0.96
0.49
0.24
0.00
0.00
0.50
0.01
0.00
0.11
0.04
n
%
23
22
5
4
7
2
0
4
0
34
24
2
2
2
1
0
0
4
6
8
0
0
16
28
15
10
41
13
4
0
0
0
0
0
0
0
26
59
6
0
4
35
14
24
3
3
1
ne
%
1
8
2
1
1
2
0
0
0
14
2
1
1
2
0
0
0
4
6
1
0
1
7
2
4
14
33
3
2
0
0
0
0
0
0
0
5
15
30
1
14
9
9
12
1
3
1
e
%
4
11
11
7
5
28
0
8
5
11
1
4
7
9
6
3
0
8
2
5
1
4
7
2
4
6
7
6
9
1
0
0
0
2
0
0
1
9
10
2
15
6
13
8
11
12
5
se
%
18
10
32
26
38
27
15
19
30
16
47
42
38
47
45
42
58
48
18
32
58
56
23
43
52
51
5
50
50
13
19
2
0
30
0
0
5
5
26
27
44
20
23
20
41
51
38
S
%
11
6
5
5
8
16
69
49
30
16
6
9
9
24
12
32
42
16
30
23
28
34
17
7
7
8
5
10
12
72
36
52
64
38
91
84
47
2
20
53
11
10
13
5
10
10
22
sw
%
4
5
2
6
4
18
16
17
28
3
3
6
7
8
3
21
0
10
19
7
13
6
14
5
3
6
1
2
5
15
42
35
36
29
9
15
7
1
6
17
10
4
8
5
5
11
15
W
%
16
17
23
34
25
5
0
2
5
3
5
25
25
3
28
1
0
6
11
9
0
0
9
6
6
4
1
3
11
0
2
11
0
1
0
1
1
1
1
0
2
5
9
12
14
6
18
nw 
-------
Mo/Da
11/21
11/22
11/23
11/24
11/25
11/26
11/27
11/28
11/29
11/30
12/ 1
12/ 2
12/ 3
12/ 4
12/ 5
12/ 6
12/ 7
12/ 8
12/ 9
12/10
12/11
12/12
12/13
12/14
12/15
12/16
12/17
12/18
12/19
12/20
12/21
12/22
12/23
12/24
12/25
12/26
12/27
12/28
12/29
12/30
12/30
I/ 1
I/ 2
I/ 3
I/ 4
I/ 5
I/ 6
I/ 7
I/ 8
U Theta
m/s deg
1.59
1.05
2.42
2.08
0.29
1.82
0.39
0.61
0.73
0.56
0.52
0.31
1.31
2.73
1.07
0.33
0.86
3.31
1.58
0.84
1.14
0.72
0.49
1.15
1.26
1.31
1.14
1.03
2.35
0.90
0.27
1.32
0.21
0.73
1.01
2.22
1.21
0.27
1.36
0.37
2.82
3.22
1.39
2.65
2.13
2.63
2.25
3.12
0.93
348
131
182
163
123
203
145
141
148
145
157
133
147
190
151
174
142
208
153
54
142
136
93
130
99
120
124
149
189
179
161
144
148
48
126
144
144
99
162
96
167
207
144
172
203
186
152
208
206
SO
w/mA2
54.8
49.5
32.2
27.7
46.9
55.7
56.7
71.2
39.6
48.5
53.0
8.4
12.1
6.7
40.5
21.9
18.9
21.3
52.9
46.6
41.3
53.1
58.4
20.0
20.6
13.2
17.3
25.6
19.4
23.8
34.3
28.1
28.1
10.7
10.5
14.3
16.0
17.1
37.6
15.7
33.7
47.8
64.3
9.0
20.2
9.9
33.0
26.6
14.8
PPT
in
0.02
0.01
0.39
0.37
0.43
0.01
0.00
0.00
0.00
0.00
0.00
1.15
0.55
1.75
0.01
0.01
0.54
0.11
0.00
0.00
0.00
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.01
0.00
0.00
0.03
0.08
0.00
0.00
0.00
0.21
0.02
0.00
0.00
0.21
0.07
0.00
0.07
0.27
0.55
0.75
0.84
1.17
n
%
59
8
1
0
15
0
6
3
2
5
3
11
4
0
1
11
2
0
0
16
0
7
20
1
1
7
0
2
0
3
8
1
12
26
6
0
1
13
0
10
0
0
0
0
0
1
0
7
10
ne
%
7
11
1
0
3
0
2
3
1
5
2
9
3
0
3
9
1
0
0
25
1
7
14
6
23
6
1
2
0
1
1
0
7
27
11
0
1
9
0
23
0
0
1
0
0
1
1
6
5
e
%
0
13
6
10
10
5
16
10
5
15
7
11
15
0
5
10
15
0
5
10
9
11
11
12
29
23
31
6
1
7
4
10
9
18
26
0
9
12
8
15
3
0
11
2
1
7
4
2
11
se
%
2
39
24
38
30
38
30
47
55
38
40
30
45
15
52
20
43
2
57
31
69
47
32
72
38
59
53
57
9
27
46
65
30
11
39
93
65
38
45
28
36
8
65
38
20
24
60
11
24
s
%
5
21
47
33
11
22
17
9
16
17
17
9
23
55
23
24
17
48
29
12
16
17
18
9
10
5
13
11
77
37
9
14
16
7
11
6
16
8
40
8
55
45
23
51
31
49
23
34
23
sw
%
6
2
16
13
6
25
10
5
5
6
8
8
6
30
6
5
8
41
8
1
3
4
3
0
0
0
2
13
13
8
2
3
9
2
2
1
5
4
6
7
7
43
1
7
27
9
6
34
18
w
%
7
5
3
6
8
10
8
9
7
6
14
7
3
1
5
10
5
8
1
3
1
2
0
0
0
1
0
3
1
7
12
4
5
1
1
0
4
4
0
5
0
2
0
0
20
6
2
6
4
nw 
-------
Appendix B-3.  Air Stagnation Episodes
                                         99
-------
Appendix B-3(a).  Puget Sound Air Deposition Study Stagnation Type One Episodes
SEQUENCE
NUMBER
7
9
15
21
23
29
37
39
43
51
53
55
59
61
73
75
77
83
85
91
95
97
99
109
111
113
115
121
125
127
129
131
135
137
139
143
145
147
149
151
155
159
161
165
167
169
171
173
179

DATE
890704
890705
890708
890711
890712
890715
890719
890720
890722
890726
890727
890728
890730
890731
890806
890807
890808
890811
890812
890815
890817
890818
890819
890824
890825
890826
890827
890830
890901
890902
890903
890904
890906
890907
890908
890910
89091 1
890912
890913
890914
890916
890918
890919
890921
890922
890923
890924
890925
890928

STAGNATION
TYPE
1
1
1







1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
MORNING
STAGNATION
TYPE
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
AFTERNOON
STAGNATION
TYPE
8
9
10
6
4
8
5
7
6
2
5
5
5
10
5
5
5
6
7
8
7
4
10
4
4
4
10
10
5
5
6
10
9
4
9
8
5
4
4
4
10
4
8
4
8
4
5
2
9
                                     101
-------
SEQUENCE
 NUMBER
              DATE
STAGNATION
   TYPE
 MORNING
STAGNATION
   TYPE
AFTERNOON
STAGNATION
   TYPE
181
185
189
195
197
211
213
215
241
243
247
249
267
289
291
305
331
339
341
349
356
357
358
359
362
372
397
401
403
405
890929 1
891001 1
891003 1
891006 1
891007 1
891014 1
891015 1
891016 1
891029 1
891030 1
891101 1
891102 1
891 1 1 1 1
891122 1
891123 1
891130 1
891213 1
891217 1
891218 1
891222 1
891225 1
891226 1
891226 1
891227 1
891228 1
900102 1
900115 1
900117 1
900118 1
900119 1




















1C
1
1
1
1C
1C
1
1
1
1
3
8
5
5
10
9
6
8
5
10
2
2
10
4
10
2
2
2
2
3
) 1
1
1
10
) 1
) 1
10
2
2
2
                                                          48 HOURS
                          102
-------
Appendix B-3(b).  Puget Sound Air Deposition Study Stagnation Type Two Episodes

SEQUENCE
NUMBER
5
7
9
11
13
15
19
21
23
25
27
29
37
39
43
49
51
52
53
55
57
59
61
65
73
75
77
79
81
83
85
89
91
95
97
99
109
111
113
115
119
121
125
127
129
131
135
137
139
143
145
147
149
151
153
155
159
161
163
165
167
169
171
173
174
177
179
181
185
187
189
191
195
197


STAGNATION
DATE
890703
890704
890705
890706
890707
890708
890710
89071 1
890712
890713
890714
890715
890719
890720
890722
890725
890726
890726
890727
890728
890729
890730
890731
890802
890806
890807
890808
890809
890810
89081 1
890812
890814
890815
890817
890818
890819
890824
890825
890826
890827
890829
890830
890901
890902
890903
890904
890906
890907
890908
890910
890911
890912
890913
890914
890915'
890916
890918
890919
890920
890921
890922
890923
890924
890925
890925
890927
890928
890929
891001
891002
891003
891004
891006
891007
TYPE
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
MORNING
STAGNATION
TYPE
2
1
1
2
2
1
2
1
1
2
2
1
1
1
1
2
1
1
1
1
2
1
1
2
1
1
1
2
2
1
1
2
1
1
1
1
1
1
1
1
2
1
1
1
1
1
1
1
1
1
1
1
1
1
Z
1
1
1
2
1
1
1
1
1
1
2
1
1
1
2
1
2
1
1
AFTERNOON
STAGNATION
TYPE
10
8
9
6
4
10
5
6

5
5
8
5
7

5
2
2 36 HOURS
5
5
10
5
-------

EQUENCE
NUMBER
205
211
213
215
223
232
233
237
239
241
243
247
248
249
250
267
275
279
281
282
288
289
291
301
303
304
305
306
307
319
325
327
328
329
330
331
332
333
334
335
336
337
338
339
340
341
342
349
354
356
357
358
359
362
372
384
392
396
397
400
401
402
403
404
405
406
407


DATE
891011
891014
891015
891016
891020
891024
891025
891027
891028
891029
891030
891101
891101
891102
891102
891111
891115
891117
891118
891118
891121
891122
891123
891128
891129
891129
891130
891130
891201
891207
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
891216
891216
891217
891217
891218
891218
891222
891224
891225
891226
891226
891227
891228
900102
900108
900112
900114
900115
900116
900117
900117
900118
900118
900119
900119
900120

STAGNATION
TYPE
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
3
2
3
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
MORNING
STAGNATION
TYPE
2
1
1
1
2
10
2
2
2
1
1
1
1
1
1
1
2
2
2
2
10
1
1
2
2
2
1
1
2
3
2
3
3
2
2
1
1
2
2
2
2
2
2
1
1
1
1
1
10
10
1
1
1
10
10
10
10
10
1
10






2
AFTERNOON
STAGNATION
TYPE
10
9
6
8
10
2
10
10
6
5
10
2
2 48
2
2
10
10
4
2
2
2
4
10
5
2
2
2 60
2
10
10
4
2
2
2
2
2
2
2
2 180
2
2
2
2
2
2
2
2
3
2
1
1 48
1
10
1
1
2
2
2
10
2
2
2
2 96
2
2
2
4















HOURS













HOURS











HOURS











HOURS











HOURS




104
-------
Appendix B-3(c).  Puget Sound Air Deposition Study Stagnation Type Three Episodes

SEQUENCE
NUMBER
5
7
9
11
13
15
19
21
23
25
27
29
37
39
43
49
51
52
53
55
57
59
61
65
73
75
77
79
81
83
85
89
91
95
97
99
109
111
113
115
119
121
125
127
129
131
135
137
139
141
143
145
147
149
151
153
155
159
161
163
165
167
169
171
173
174
177
179
181
182
185
187
189
191


DATE
890703
890704
890705
890706
890707
890708
890710
890711
890712
890713
890714
890715
890719
890720
890722
890725
890726
890726
890727
890728
890729
890730
890731
890802
890806
890807
890808
890809
890810
890811
890812
890814
890815
890817
890818
890819
890824
890825
890826
890827
890829
890830
890901
890902
890903
890904
890906
890907
890908
890909
890910
89091 1
890912
890913
890914
890915
890916
890918
890919
890920
890921
890922
890923
890924
890925
890925
890927
890928
890929
890929
891001
891002
891003
891004

STAGNATION
TYPE
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
MORNING
STAGNATION
TYPE
2
1
1
2
2
1
2
1
1
2
2
1
1
1
1
2
1
1
1
1
2
1
1
2
1
1
1
2
2
1
1
2
1
1
1
1
1
1
1
1
2
1
1
1
1
1
1
1
1
3
1
1
1
1
1
2
1
1
1
2
1
1
1
1
1
1
2
1
1
1
1
2
1
2
AFTERNOON
STAGNATION
TYPE
10
8
9
6
4
10
5
6
4
5
5
8
5
7
6
5
2
2 36 HOURS
5
5
10
5
10
10
5
5
5
5
6
6
7
5
8
7
4
10
4
4
4
10
5
10
5
5
6
10
9
4
9
7
8
5
4
4
4
4
10
4
8
5
4
8
4
5
2
2
6
9
3
3
8
8
5
10
                                       105
-------
PUGET SOUND AIR DEPOSITION STUDY
  STAGNATION TYPE  THREE EPISODES

EQUENCE
NUMBER
195
197
205
211
213
215
217
223
232
233
237
239
241
243
247
248
249
250
267
275
279
281
282
288
289
291
299
301
303
304
305
306
307
319
325
327
328
329
330
331
332
333
334
335
336
337
338
339
340
341
342
349
350
354
356
357
358
359
362
367
372
384
388
392
396
397
400
401
402
403
404
405
406
407


DATE
891006
891007
891011
891014
891015
891016
891017
891020
891024
891025
891027
891028
891029
891030
891101
891101
891102
891102
891111
891115
891117
891118
891118
891121
891122
891123
891127
891128
891129
891129
891130
891130
891201
891207
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
891216
891216
891217
891217
891218
891218
891222
891222
891224
891225
891226
891226
891227
891228
891231
900102
900108
900110
900112
900114
900115
900116
900117
900117
900118
900118
900119
900119
900120

STAGNATION
TYPE
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
HORNING
STAGNATION
TYPE
1
1
2
1
1
1
3
2
10
2
2
2
1
1
1
1
1
1
1
2
2
2
2
10
1
1
3
2
2
2
1
1
2
3
2
3
3
2
2
1
1
2
2
2
2
2
2
1
1
1
1
1
1
10
10
1
1
1
10
3
10
10
10
10
10
1
10
1
1
1
1
1
1
2
AFTERNOON
STAGNATION
TYPE
5
10
10
9
6
8
4
10
2
10
10
6
5
10
2
2
2
2
10
10
4
2
2
2
4
10
10
5
2
2
2
2
10
10
4
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
3
3
2
1
1
1
10
1
10
1
2
3
2
2
10
2
2
2
2
2
2
2
4
















48 HOURS














60 HOURS











192 HOURS


























96 HOURS




              106
-------
Appendix B-4.  Data for Air Stagnation Analysis
ABBREVIATIONS USED IN THE APPENDIX

T = PRECIPITATION TYPE (1 = NO PRECIPITATION
                      (2 = PRECIPITATION
FIRST T = MORNING PRECIPITATION/NO PRECIPITATION
SECOND T = AFTERNOON PRECIPITATION/NO PRECIPITATION

AM MIX HGHT = MORNING MIXING HEIGHT
AM LYR WND  = MORNING MIXING LAYER WIND
AM SFC WND  = MORNING SURFACE WIND
PM MK HGHT = AFTERNOON MIXING HEIGHT
PM LYR WND  = AFTERNOON MIXING LAYER WIND
PM SFC WND  = AFTERNOON SURFACE WIND

SEASON

1 = DECEMBER - FEBRUARY
2 = MARCH - MAY
3 = JUNE - AUGUST
4 = SEPTEMBER - NOVEMBER
                               107
-------
        REGION 10 PUGET SOUND AIR  DEPOSITION  STUDY
MIXING HEIGHTS ARE IN METERS AND WIND  SPEEDS  IN METERS/SEC
11:34 MONDAY,  JUNE 10,  1991
TAT I ON


72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
YEAR


89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
MONTH


7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
SEASON


3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
DAY


1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
T


2
2






2
1
1
1
1
1
1
2
2
2
1
1
2
1
1
1
1
1
1
1
1
1
1
2
1
2
1
1
1
1
1
1
1
1
1
1
1
1
2
1
1
1
2
2
AM
MIX
HGHT
372
250
244
241
124
152
520
477
138
652
145
141
546
530
481
435
581
549
326
103
455
129
1119
590
564
457
296
135
592
101
112
167
190
395
634
673
103
89
372
654
310
102
99
557
589
248
617
290
366
377
483
302
AM
LYR
WND
5.6
3.2
2.4
2.0
0.2
2.9
1.3
0.8
0.3
0.7
0.0
0.3
1.2
1.3
0.4
3.9
3.7
3.5
0.0
1.1
3.0
1.3
2.1
3.7
1.5
1.0
1.9
0.9
1.3
0.2
0.9
2.6
2.7
0.8
2.2
2.6
1.8
1.6
1.0
2.0
2.1
0.4
0.2
2.5
1.3
0.0
3.6
1.9
1.5
0.0
2.0
2.5
AM
SFC
UNO
5.0
2.8
1.8
1.5
0.2
1.8
1.1
0.5
0.3
0.4
0.0
0.3
0.5
1.1
0.4
3.3
1.8
2.4
0.0
.1
.3
.3
.6
.8
1.6
1.1
0.9
0.9
0.6
0.2
0.9
1.6
1.6
0.5
2.3
2.1
1.8
1.6
1.1
1.9
1.0
0.4
0.2
2.0
1.0
0.0
2.6
1.8
2.0
0.0
2.0
2.4
T


2
2
2
1
1
1
1
2
1
1
1
1
1
1
1
2
1
2
1
1
2






1
2
1
2
1
2
2
1
1
1
1
1
1
1
1
1
2
1
1
2
1
1
2
2
2
PM
MIX
HGHT
444
1434
1470
1984
2127
1532
697
1587
1061
1404
1928
836
1443
1402
1707
775
1296
954
1208
1461
1822
1776
1249
968
1289
498
970
1441
1589
1368
688
1696
974
1788
1541
1098
863
863
794
1070
1676
1779
1495
1304
1480
1586
1532
1185
739
562
529
473
PM
LYR
UNO
4.8
4.9
4.9
4.1
3.6
3.1
2.6
1.9
3.0
2.8
3.4
2.6
4.0
3.6
4.5
3.4
5.3
2.2
3.2
4.3
3.1
3.6
4.4
4.1
3.3
2.5
4.7
3.1
3.5
2.7
3.2
3.5
1.9
3.6
4.5
3.7
4.9
4.2
4.1
3.8
3.5
2.7
4.7
3.1
3.1
5.0
4.0
4.3
2.5
4.5
3.2
3.4
PM
SFC
WND
3.4
3.2
2.9
2.1
3.2
2.7
1.6
1.7
1.9
2.1
2.1
1.7
2.9
2.2
3.8
2.7
3.4
1.4
2.4
2.6
2.6
3.0
3.1
2.6
2.6
2.0
4.8
1.9
1.7
1.9
2.1
2.8
1.8
3.2
2.7
2.9
3.1
2.7
3.1
2.4
2.1
1.6
3.4
2.2
1.9
3.1
2.3
3.2
1.4
4.9
2.8
2.3
                           109
-------
        REGION 10 PUGET  SOUND  AIR DEPOSITION STUDY
MIXING HEIGHTS ARE IN  METERS AND WIND SPEEDS IN METERS/SEC
11:34 MONDAY,  JUNE 10,  1991
TAT I ON


72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
YEAR


89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
MONTH


8
8
8
8
8
8
8
8
8
8
9
9
9
9
•9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
10
10
10
10
10
10
10
10
10
10
10
10
SEASON


3
3
3
3
3
3
3
3
3
3
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
DAY


22
23
24
25
26
27
28
29
30
31
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
1
2
3
4
5
6
7
8
9
10
11
12
T


2
1
1
1
1
1
2
1
1
2
1
1
1
1
2
1
1
1
1
1
1
1
1
1
1
1
2
1
1
1
1
1
1
1
1
2
1
1
1
2
1
1
1
1
2
1
1
2
2
2
1
2
AM
MIX
HGHT
155
529
298
106
244
278
794
323
394
251
108
298
488
145
82
84
104
76
118
90
90
62
70
74
290
433
105
90
147
185
114
75
60
75
402
203
284
94
80
309
67
97
255
255
413
156
161
469
258
655
456
519
AM
LYR
UND
0.9
2.4
1.5
0.4
1.6
1.0
0.9
2.6
1.7
1.8
0.2
0.6
0.9
0.5
2.0
1.0
1.8
0.6
5.2
1.4
1.8
0.6
0.0
0.6
2.3
0.0
0.0
0.0
1.1
2.7
0.9
1.2
1.1
0.3
1.8
2.6
2.3
0.7
0.4
2.6
1.9
.2.4
1.4
3.0
3.9
1.5
1.4
1.2
2.1
1.7
4.0
3.9
AM
SFC
UND
0.9
1.0
1.0
0.4
1.8
0.5
0.4
2.6
1.4
0.9
0.2
0.3
0.3
0.5
2.0
1.0
1.8
0.6
5.2
1.4
1.8
0.6
0.0
0.6
1.1
0.0
0.0
0.0
1.1
1.6
0.9
1.2
1.1
0.3
2.2
2.1
2.0
0.7
0.4
2.7
1.9
2.4
0.7
1.7
2.7
1.0
0.3
0.4
2.1
1.4
2.3
3.8
T


1
1
1
1
1
2
2
1
2
2
1
1
1
2
1
1
1
1
1
1
1
1
1
1
1
2
2
1
1
1
1
1
1
1
1
2
1
1
1
1
1
1
1
2
2
1
2
2
1
2
2
2
PM
MIX
HGHT
1435
1185
863
819
695
550
938
1232
560
923
1285
1451
1617
528
1068
2204
1000
1954
1161
1930
1042
673
711
592
669
1155
1899
613
1749
1423
622
1750
519
1129
473
684
1998
2205
319
1254
1532
1738
1192
1192
646
1117
815
829
726
1040
795
1199
PM
LYR
UND
2.7
3.2
3.4
3.7
2.7
2.5
3.5
4.0
2.8
3.4
2.6
3.3
3.0
3.3
3.5
68.3
2.6
7.7
5.3
4.3
3.5
2.5
2.3
3.3
3.3
2.4
3.0
3.9
5.1
2.8
2.6
4.1
2.2
3.0
3.5
2.0
2.9
3.1
5.3
3.6
5.1
4.8
3.2
4.3
1.4
2.3
2.9
2.1
3.2
3.1
6.4
2.3
PM
SFC
UND
1.9
1.8
2.3
2.4
1.9
1.5
2.9
2.9
1.9
1.8
1.3
2.1
2.3
2.6
2.2
3.7
1.6
5.5
3.4
3.1
2.2
1.5
1.6
2.2
2.1
1.2
1.8
2.6
2.8
2.1
2.1
1.9
1.9
2.9
3.0
1.5
1.7
1.6
3.4
2.6
3.4
2.9
2.4
2.9
1.3
1.2
1.8
1.7
2.1
2.7
4.7
2.1
                           110
-------
        REGION 10 PUGET SOUND  AIR  DEPOSITION STUDY
MIXING HEIGHTS ARE IN METERS AND WIND  SPEEDS IN METERS/SEC
11:34 MONDAY,  JUNE 10,  1991
TAT I ON

72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
YEAR

89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
MONTH

10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
11
12
12
12
SEASON

4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
1
1
1
DAY

13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
1
2
3
T

2
1
1
1
1
2
2
1
2
2
2
2
1
2
1
1
1
1
2
1
1
2
2
2
2
2
2
2
2
1
2
2
2
1
2
1
1
2
2
2
1
1
2
2
2





2
2
AM
MIX
HGHT
289
94
95
74
163
515
95
122
122
149
84
94
103
539
156
161
153
173
193
115
96
507
862
91
241
82
557
426
385
344
361
378
403
403
403
403
427
481
210
138
110
110
82
83
134
469
120
131
135
123
272
421
AM
LYR
WND
2.3
0.5
1.6
1.4
5.0
3.3
2.4
2.6
5.1
5.6
4.9
3.6
2.5
3.3
2.7
3.6
1.1
1.5
3.7
1.3
1.9
4.7
7.4
1.0
3.3
2.2
7.8
7.0
7.4
1.3
2.3
5.1
5.8
3.1
2.9
2.4
2.8
4.0
2.5
0.9
1.3
1.9
2.4
2.4
0.9
4.3
3.0
3.2
1.9
2.7
8.9
8.1
AM
SFC
WND
2.0
0.5
1.6
1.4
3.8
2.0
2.4
2.6
5.1
5.6
4.9
3.6
2.5
4.0
2.4
2.2
0.6
0.9
2.9
1.3
1.9
3.2
4.0
1.0
2.6
2.2
5.4
5.3
4.5
1.1
2.0
3.1
3.0
1.6
1.3
1.7
2.0
3.4
1.4
0.9
1.3
1.9
2.4
2.4
0.9
2.4
3.0
3.2
1.9
2.7
5.4
6.0
T

2
1
1
1
1
2
1
2
3
2
3
1
2
2
2
1
1
2
1
1
1
2
1
2
2
2
2
2
2
2
1
2
1
2
2
1
1
2
2
1
1
2
2
2
2
2
1
1
1
2
3
2
PM
MIX
HGHT
1109
2053
1562
1697
992
1045
1434
465
356
246
496
496
745
Tib
1506
1581
1244
396
1309
818
467
556
892
923
514
1464
731
505
505
278
723
1184
792
792
792
792
400
534
231
878
706
533
373
388
1092
808
677
678
316
228
294
360
PM
LYR
WND
3.0
4.1
3.0
4.3
2.5
4.5
3.6
5.7
6.6
5.6
11.2
3.6
5.6
2.2
3.5
2.4
2.6
2.1
2.3
1.8
3.5
6.0
2.4
3.5
4.9
5.8
6.0
7.2
1.8
3.4
2.9
4.4
2.8
2.8
3.2
3.1
2.6
2.0
5.0
1.6
3.0
4.0
3.6
2.3
3.9
5.8
4.6
2.0
2.7
5.0
13.9
9.6
PM
SFC
WND
1.9
2.6
1.8
3.1
1.9
3.4
2.2
4.5
4.5
4.6
4.1
2.7
4.6
2.4
2.1
1.2
1.6
2.1
2.1
1.5
2.4
4.4
1.3
2.9
3.2
3.9
5.4
5.6
1.1
2.8
2.7
3.2
1.8
1.8
1.9
2.0
2.6
1.5
3.3
1.2
2.0
2.7
2.5
1.6
2.8
2.9
3.0
2.0
2,4
4.1
5.8
6.9
                           111
-------
        REGION 10 PUGET  SOUND AIR DEPOSITION STUDY
MIXING HEIGHTS ARE IN  METERS AND WIND SPEEDS IN METERS/SEC
11:34 MONDAY,  JUNE 10,  1991
;TATION


72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
72797
YEAR


89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
89
90
90
90
90
90
90
90
90
90
90
90
90
90
90
90
90
90
90
90
90
90
90
90
90
MONTH


12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
12
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
SEASON


1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
DAY


4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
T


2
2
2
1
2
2
1
1
1
1
1
1
1
1
1
2
2
2
1
2
2
2
1
1
2
2
2
1
2
2
2
2
1
2
2
2
2
2
1
2
2
2
1
2
1
1
1
1
2
2
2
2
AM
MIX
HGHT
262
529
694
340
77
893
197
191
243
111
197
515
191
160
134
407
684
258
106
491
341
200
83
213
97
294
375
229
98
82
442
131
501
416
284
151
362
265
167
103
142
439
388
73
126
126
126
178
434
302
1027
724
AM
LYR
WND
4.7
3.5
2.8
4.3
1.5
5.5
2.2
4.6
2.8
1.7
2.2
0.5
2.1
1.4
1.9
2.1
2.4
4.5
1.8
5.1
1.3
3.2
0.5
1.2
1.0
0.8
0.9
4.2
1.8
3.0
4.3
6.1
7.3
5.0
6.4
5.2
7.4
5.4
6.5
2.7
2.1
3.3
1.3
2.6
1.9
1.9
1.9
2.1
1.8
7.1
7.2
6.5
AM
SFC
WND
5.4
1.7
2.6
2.3
1.5
3.3
2.4
2.7
1.4
1.7
0.3
0.0
1.1
1.4
1.9
1.1
1.3
2.8
1.8
3.1
1.5
1.4
0.5
0.6
1.0
0.4
0.9
2.8
1.8
3.0
3.0
6.1
4.3
3.9
5.2
3.6
4.5
3.0
5.4
2.7
2.1
3.0
0.6
2.6
1.9
1.9
1.9
1.1
1.0
5.4
5.6
2.8
T


3
2
2
2
2
1
1
1
1
1
1
1
1
1
1
2
2
2
1
2
1
1
1
2
1
2
1
2
3
1
2
3
2
1
3
1
3
1
2
1
2
1
2
1
1
1
1
1
2
3
1
2
PM
MIX
HGHT
74
473
607
432
744
1570
772
872
353
614
517
671
263
449
421
888
647
405
353
591
884
258
276
548
327
872
708
425
225
172
1100
185
661
509
293
76
193
193
310
215
224
635
318
499
499
499
680
532
372
181
1493
1322
PM
LYR
WND
9.3
4.2
3.3
4.8
6.5
5.8
3.5
2.0
2.3
1.6
1.3
1.4
2.3
2.5
2.5
3.3
3.5
2.7
5.0
6.0
1.4
1.7
1.6
2.2
1.3
1.3
2.7
5.2
12.0
2.0
4.2
11.4
6.4
6.4
11.5
4.0
11.4
5.4
3.8
2.8
3.8
1.4
3.8
3.5
3.5
3.5
1.9
2.2
6.1
16.5
7.4
7.0
PM
SFC
WND
2.9
2.8
2.0
3.4
3.8
2.1
2.9
1.1
1.4
0.7
0.1
0.8
1.7
1.7
1.7
2.1
2.3
1.9
2.9
1.8
1.4
1.4
1.0
1.8
1.1
0.7
1.8
3.3
3.6
2.5
4.3
3.5
4.9
5.0
4.2
4.0
3.3
4.5
3.1
2.1
3.1
0.8
3.0
2.4
2.4
2.4
1.7
1.4
4.6
5.7
3.2
5.2
                          112
-------
                           REGION 10 PUGET SOUND AIR DEPOSITION  STUDY              11:34  MONDAY,  JUNE  10,  1991
                   MIXING HEIGHTS ARE IN METERS AND WIND SPEEDS  IN  METERS/SEC

STATION    YEAR    MONTH    SEASON    DAY    T    AM      AM     AM     T    PM       PM      PM
                                                  MIX     LYR    SFC        MIX      LYR    SFC
                                                  HGHT    WND    WND        HGHT     WND    UNO
72797
72797
72797
72797
72797
72797
72797
90
90
90
90
90
90
90





1
1
1
1





25
26
27
28
29
30
31
2
2
2
2
2
2
1
526
177
345
519
528
528
528
7.8
3.8
7.9
4.8
6.4
5.3
5.9
5.8
2.3
6.3
4.5
6.7
2.6
3.4
2
2
2
2
3
2
3
575
254
608
612
638
664
106
5.0
4.8
7.3
8.9
5.4
5.1
6.7
3.4
3.9
4.9
6.9
3.7
3.9
4.6
                                                   113
-------
Appendix C.   Laboratory Results - Six-Month Aerosol  and
Deposition Study	


      C-l.  Sampling and Analysis Protocols	117
      C-2.  Sample Selection for Analysis	119
      C-3.  Total Suspended Participate Data	123
      C-4.  Elemental Aerosol Concentrations   	135
      C-5.  Participate PAH Concentrations	143
      C-6.  Vapor PAH Concentrations  	153
      C-7.  Particulate and Vapor Aliphatics and PCBs	159
      C-8.  Deposition Metals	165
      C-9.  Nutrient Data	171
      C-10. Concentrations of Aliphatic Hydrocarbons and PCS
           Congeners in Deposition Samples	177
      C-ll. PAH Deposition Data	181
      C-12. Quality Control for Chemical Analysis	189
                                     115
-------
Appendix C-l.  Sampling and Analysis Protocols
Aerosol Sampling

Aerosol samples for the six-month study were collected with General Metal Works Model PS-
1 aerosol samplers (U.S. EPA, 1988).  The samplers were equipped with 102-mm-diameter
quartz high purity filters and backed up  with  6-cm-diameter, 8-cm-long polyurethane foam
plugs (PUFs) for collection of organic vapor.

The methods for cleaning PUFs and filters were taken from the U.S. EPA (1988) Compendium
Method TO-13.  All PUFs were cleaned  with  solvent (pesticide grade acetone) in a Soxhlet
extractor  for  14  to 24  hours, cycling  at four cycles per  hour.   The  cleaned PUFs were
transferred to clean, glass cartridge  holders; wrapped in aluminum foil;  and  stored in 1-liter
glass jars with foil-lined lids until used.  The glass cartridges and jars, as well as the aluminum
foil, were precleaned by ashing at 600°C  for five hours before use.

Filters were cleaned by soaking in methylene chloride for 12 hours, air drying for 15 minutes,
and then ashing in 8-ounce glass jars at 600°C for five hours. After cooling, jars were sealed
with lids  containing Teflon liners rinsed in methylene chloride and stored until Teflon filters
were  to  be used.  Each lot of filters was checked for acceptability by first cleaning with
methylene chloride and then analyzing a sample filter as a field sample.

Deposition Sampling

A large  water-filled Pyrex pan  with a surface area of 0.12 m2  was used  as a  deposition
collector.  The pan contained a  1-cm  layer of high purity water to prevent dry deposited
material  from blowing out of the pan during dry windy weather.  A reservoir of water  was
used to maintain a constant level of water  in the pan in dry weather and an overflow drain
and reservoir collected the excess water in wet weather.  The contents in the deposition pan
were  transferred biweekly to the deposition reservoir container and taken to the laboratory for
storage in a refrigerator.  Deposition samples were acidified to less than 2 pH with Baker Insta-
Analyzed hydrochloric acid  and  held at  4°C  in  the dark until analyzed.   The  deposition
sampling equipment was  made  of glass  or Teflon and was  acid-cleaned  in a 1:1 nitric
acid:distilled water  solution and  then solvent-rinsed with methylene chloride.  Cleaned pans
were sealed in clean polyethylene bags until used.
                                           117
-------
Appendix C-2.  Sample Selection for Analysis
Aerosols

Due to budget constraints, it was necessary to limit the number of sample analyses.  All 184
of the aerosol samples collected were weighed for determination of total mass; 51 of the aerosol
samples were analyzed for metals and PAHs;  and  10 of the aerosol samples were further
analyzed for both vapor and paniculate PAHs, PCBs, and aliphatic compounds.

A sample selection committee met several times during the course of the study to  determine
which samples should be analyzed.  The following criteria were developed for aerosol sample
selection during the first intensive sampling period using the total mass of each sample as the
comparative criterion.

Sample analysis criteria - first intensive period:

       1.  The two highest, the  two lowest, and the two weights closest to the mean were
       analyzed  from the Alexander Avenue site.   This selection determined the set of all
       possible dates for selecting samples from the remaining sites.

       2.  One of the two highest weight days (ordinarily the highest of all) and one of the two
       lowest weight days (usually the lowest) were then analyzed at all of the remaining sites.
       If  the highest  or lowest weight day coincided with  lost  data at other sites, the next
       highest or lowest weight day was chosen.

       3.  Samples from the remaining sites were analyzed for the  day displaying the median
       weight at the Alexander Avenue site. If the total number of days in the sampled period
       was even, then a coin was flipped to chose which of the two near-median weights at the
       Alexander Avenue site would be selected  to guide the choice of the analyses at the other
       sites.

Using these criteria, the samples presented in Table 1 were selected for analyses from the first
intensive period.

Similar criteria were used to  select the samples analyzed for the nonintensive period and the
second intensive period.


Table 1. Selected Aerosol Samples - First Intensive Period	

Starting Day  AS	SL	MS	TM	RS	

7/24          *
7/27          *               *              *              *             *
8/03          *
g/14          *****

8/17          *
8/21          *****

During the nonintensive period, only three aerosol samplers were operating; Alexander Avenue,
Tyee Marina, and Brown's Point  (BP).  The  aerosol  samples contained in Table 2 were
analyzed for the nonintensive period.
                                          119
-------
Table 2. Selected Aerosol Samples - Nonintensive Period
Starting
Day
9/11
9/18
8/28
9/14
11/6
11/9
AS
*
*
*
*
*
*
TM BP
* *

* *


*
The following aerosol samples (Table 3) were selected for the second intensive period according
to the criteria outlined above.

Table 3. Selected Aerosol Samples - Second Intensive Period
Starting
Day
12/11
12/13
12/18
11/16
12/04
12/15
AS
*
*
*
*
*
*
SL MS TM
* * *


* * *

* *
RS
*


*

*
      NOTE: The abbreviations in the above tables are translated as follows:  Tyee
      Marina (TM), Morse Industrial Supply (MS), Sea-Land (SL), Alexander Avenue
      (AS), and Riverside School  (RS).

In addition to the  samples presented above,  the  following samples were analyzed for  the
indicated reasons:

      1. Samples collected from November 27 to 30 from the Alexander Avenue and Riverside
      School  sites:  These  samples were taken during the  highest aerosol readings that
      occurred during the study.  The samples were analyzed to determine from the chemical
      patterns which sources were the major contributors to the high readings.

      2.  Samples  collected  from September 7  to 11  and September  14  to 18 from  the
      Alexander Avenue site: These samples were analyzed to composite the results with the
      September 11  to  14 and September 18 to 21 samples to  compare the  aerosol and
      deposition measurements for the same time period during a two-week dry  period.

      3. Samples from November  2 to 6 and November 13 to 16 from the Alexander Avenue
      site:  These samples were analyzed to composite the results with the November 6 to 9
      and November 9 to 13 samples to compare the aerosol and deposition measurements for
      the same time period during a two-week period of heavy and continuous rain.

      4. November 30 to December 4, December 4 to 7, December 7 to 11, and December
      12 to 13 samples were analyzed to composite their results with the December 11 to 12
      and December 13  to 14 samples. This was done to compare the results with the aerosol
      results from the receptor modeling study.


                                        120
-------
PCBs and Aliphatic Compounds

The aerosol and deposition samples that were analyzed for PCBs and aliphatic compounds are
presented in Table 4.
Table 4. PCS and Aliphatic Analyses
Starting
Day
Sites
7/24
12/11
AS, TM, SL, and MS
AS, TM, SL, MS, RS, and AS (duplicate)
Deposition

Fifty of the deposition samples were  analyzed for metals and PAHs and ten were further
analyzed for PCBs and aliphatic compounds (see above).

The deposition samples presented in Table 5 were analyzed for metals and PAHs. The time
periods were chosen to coincide with the intensive sampling periods.
Table 5.  Selected Deposition Samples
Starting
Day
7/13
7/27
8/10
8/24
9/7
11/2
11/16
11/30
12/14
AS SL
* *
* *
* *
* *
* *
* *
* *
* *
* *
MS
*
*
*
*
*
*
*
*
*
TM
*
*
*
*
*
*
*
*
*
DTM
*
*
*

*




RS
*
*
*
*
*
*
*
*
*
 Note: Duplicate Tyee Marina (DTM)
                                        121
-------
Appendix C-3. Total Suspended Particulate Data
                                        123
-------
                       Puget  Sound Water  Quality  Authority
                       Total  Suspended  Particulate  Data
                       (corrected for standard temperature and pressure)
Ul
Sample Flow
On
Date
PSAPCA
06-29
07-03
07-06
07-10
07-13
07-17
07-20
07-24
07-27
07-31
08-03
08-07
08-10
08-14
08-17
08-21
08-24
08-28
09-01
09-05
09-07
09-11
09-14
09-18
09-21
09-25
09-28

Time
(Alex)
1230
1745
1410
1440
1745
1605
1315
1550
1910
1640
1715
1440
1650
1355
1320
1410
1005
1140
1000
1130
1430
920
755
1428
2135
2149
945

Mag
;
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
R
Temp

528.58
527.58
533.58
527.58
532.58
531.58
527.58
535.58
527.58
525.58
533.58
538.58
532.58
533.58
528.58
531.58
519.58
524.58
519.58
530.58
539.58
523.58
515.58
526.58
526.58
519.58
516.58

Pres

29.84
30.02
30.10
29.96
30.10
30.02
30.04
30.02
30.05
29.87
30.46
30.44
30.45
30.49
30.38
30.15
30.54
30.48
30.35
30.03
29.89
30.48
30.41
30.42
30.46
30.37
30.54
M
Std

7.11
7.14
7.11
7.14
7.12
7.12
7.14
7.09
7.15
7.14
7.15
7.12
7.16
7.16
7.18
7.13
7.26
7.22
7.24
7.00
7.10
7.22
7.27
7.20
7.20
7.24
7.28
Off
Date

07-03
07-06
07-10
07-13
07-17
07-20
07-24
07-27
07-31
08-03
08-07
08-10
08-14
08-17
08-21
08-24
08-28
09-01
09-05
09-07
09-11
09-14
09-18
09-21
09-25
09-28
10-02
Time

1730
1410
1425
1715
1500
1310
1500
1854
1540
1705
1430
1640
1350
1300
1400
950
1130
955
1120
1222
905
745
1420
2054
2137
920
1514
Mag

45
47
47
48
46
45
48
48
45
47
46
48
45
47
46
52
45
44
44
46
47
50
42
44
44
46
44
R
Temp

527.58
533.58
527.58
532.58
531.58
527.58
535.58
527.58
525.58
533.58
538.58
532.58
533.58
528.58
531.58
519.58
524.58
519.58
530.58
539.58
523.58
515.58
526.58
526.58
519.58
516.58
516.58

Pres

30.02
30.10
29.96
30.10
30.02
30.04
30.02
30.05
29.87
30.46
30.44
30.45
30.49
30.38
30.15
30.54
30.48
30.35
30.03
29.89
30.48
30.41
30.42
30.46
30.37
30.54
30.53
M
Std

6.78
6.89
6.92
6.97
6.82
6.78
6.95
7.00
6.77
6.94
6.83
7.01
6.79
6.96
6.84
7.40
6.85
6.79
6.74
6.95
7.00
7.27
6.60
6.77
6.79
6.98
6.83
Mean
M Std

6.95
7.02
7.02
7.06
6.97
6.95
7.05
7.05
6.96
7.04
6.99
7.07
6.98
7.06
7.01
7.27
7.06
7.01
6.99
6.98
7.05
7.25
6.94
6.99
7.00
7.11
7.06
Cal.
Curve

37.9
37.9
37.9
37.9
37.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
71.9
27.6
Inter- Rate.at STP
cept

-1.89
-1.89
-1.89
-1.89
-1.89
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
-9.74
0.488
m /mi n

0.233
0.235
0.235
0.236
0.234
0.232
0.233
0.233
0.232
0.233
0.233
0.234
0.232
0.234
0.233
0.237
0.234
0.233
0.233
0.232
0.234
0.236
0.232
0.233
0.233
0.234
0.238
Total
Minutes

6325
5718
5776
4413
5592
4143
5890
4503
5549
4342
5596
4442
5581
4532
5794
4032
5845
5653
5837
3029
5420
4224
6146
4695
5771
3569
6088
Correct
Volume
m3

1474.44
1343.50
1357.13
1041.54
1307.26
961.71
1375.02
1051.22
1288.85
1013.33
1302.10
1038.22
1297.45
1058.94
1349.78
953.60
1365.32
1316.54
1358.18
704.17
1265.67
997.84
1425.38
1092.13
1343.22
836.41
1448.55
Filter
Weight
g

0.0373
0.0269
0.0596
0.0644
0.0469
0.0548
0.0678
0.0923
0.1131
0.0752
0.0855
0.0850
0.0748
0.0728
0.0637
0.0424
0.0699
0.0810
0.0473
0.0638
0.0974
0.1224
0.0867
0.1035
0.1251
0.0589
0.0702

TSP
ug/m

25.30
20.02
43.92
61.83
35.88
56.98
49.31
87.80
87.75
74.21
65.66
81.87
57.65
68.75
47.19
44.46
51.20
61.52
34.83
90.60
76.96
122.67
60.83
94.77
93.13
70.42
48.46
-------
to
Sample Flow
On
Date
PSAPCA
10-02
10-05
10-09
10-12
10-16
10-19
10-23
10-26
10-30
11-02
11-06
11-09
11-13
11-16
11-20
11-23
11-27
11-30
12-04
12-07
12-11
12-11
12-12
12-13
12-14
12-14
12-15
12-16
12-18
12-21
12-23
12-25
01-02
01-05

Time Mag
R
Temp

Pres
M
Std
Off
Date
Time
Mag
R
Temp

Pres
M
Std
Mean
M Std
Cal.
Curve
Inter- Rate,at STP
cept
m /min
Total
Minutes
Correct
Vol ume
3
m
Filter
Weight
9

TSP
ug/m
(Alex), cont'd:
1525 50
1318 50
2110 50
1540 50
2140 50
1540 50
2055 50
0830 50
1237 50
2115 50
1950 50
0810 50
1919 50
2045 50
1312 50
1234 50
1425 50
0015 50
2130 50
0735 50
2015 50
PUF Plug
1510 50
1452 50
2110 50
PUF Plug
1525 50
1732 50
1755 50
1708 50
3120 50
1830 50
1805 50
1640 50
516.58
521.58
517.58
519.58
509.58
513.58
509.58
507.58
502.58
498.58
504.58
511.58
505.58
501.58
509.58
503.58
513.58
499.58
505.58
499.58
487.58

496.58
501.58
493.58

497.58
497.58
497.58
502.58
501.58
501.58
498.58
512.58
30.53
30.49
30.62
30.42
30.06
29.93
29.56
29.80
30.21
30.18
29.70
29.98
29.92
30.02
29.90
29.60
30.29
30.25
29.94
29.98
30.38

30.31
30.27
30.24

30.20
29.97
29.97
30.23
30.43
30.25
30.13
29.88
7.28
7.24
7.28
7.25
7.27
7.23
7.21
7.26
7.34
7.37
7.26
7.25
7.28
7.33
7.25
7.26
7.27
7.37
7.29
7.34
7.47

7.40
7.36
7.41

7.38
7.35
7.35
7.34
7.38
7.35
7.36
7.23
10-05
10-09
10-12
10-16
10-19
10-23
10-26
10-30
11-02
11-06
11-09
11-13
11-16
11-20
11-23
11-27
11-30
12-04
12-07
12-11
12-12
12-14
12-13
12-14
12-15
12-18
12-16
12-18
12-21
12-23
12-25
12-28
01-05
01-09
1314
2055
1530
2130
1504
1940
0820
1230
2101
1925
0740
1906
2030
1302
1215
1415
0005
2042
0710
2005
2005

1448
2000
1520

1720
1735
1651
1315
1820
1310
1620
1855
44
41
45
42
39
45
50
42
38
44
46
49
37
43
44
40
12
37
48
15
46

48
50
46

50
50
42
40
53
41
44
48
521.58
517.58
519.58
509 . 58
513.58
509 . 58
507.58
502.58
498.58
504.58
511.58
505.58
501.58
509.58
503 . 58
513.58
499.58
505.58
499.58
487.58
496.58

501.58
493.58
497.58

497.58
497.58
502.58
501.58
501.58
502.58
512.58
499.58
30.49
30.62
30.42
30.57
29.93
29.56
29.80
30.21
30.18
29.70
29.98
29.92
30.02
29.90
29.60
30.29
30.25
29.94
29.98
30.38
30.31

30.27
30.24
30.20

29.97
29.97
30.23
30.43
30.25
30.28
29.88
29.80
6.79
6.59
6.87
6.72
6.38
6.84
7.26
6.73
6.42
6.82
6.95
7.21
6.30
6.73
6.81
6.50
3.61
6.27
7.19
4.09
7.10

7.21
7.41
7.08

7.35
7.35
6.73
6.60
7.57
6.66
6.78
7.17
7.04
6.92
7.08
6.99
6.83
7.04
7.23
6.99
6.88
7.09
7.11
7.23
6.79
7.03
7.03
6.88
5.44
6.82
7.24
5.71
7.29

7.30
7.38
7.24

7.36
7.35
7.04
6.97
7.47
7.00
7.07
7.20
27.6
27.6
27.6
27.6
27.6
27.6
27.6
27.6
27.6
27.6
27.6
27.9
27.9
27.9
27.9
27.9
27.9
32.1
32.1
32.1
32.1

32.1
32.1
32.1

32.1
32.1
32.1
35.9
35.9
35.9
29.2
29.2
0.488
0.488
0.488
0.488
0.488
0.488
0.488
0.488
0.488
0.488
0.488
0.367
0.367
0.367
0.367
0.367
0.367
0.145
0.145
0.145
0.145

0.145
0.145
0.145

0.145
0.145
0.145
-1.12
-1.12
-1.12
0.137
0.137
0.237
0.233
0.239
0.235
0.230
0.237
0.244
0.236
0.232
0.239
0.240
0.246
0.230
0.239
0.239
0.234
0.182
0.208
0.221
0.174
0.222

0.223
0.226
0.221

0.225
0.224
0.215
0.225
0.239
0.226
0.237
0.242
4190
6163
3982
6111
3924
6018
3622
6149
4733
5637
3589
6429
4389
5276
4267
5910
4691
5671
3458
6542
1103

1419
1754
1087

1562
2880
4256
2643
3178
3999
4215
5896
993.91
1435.13
950.34
1438.52
901.45
1427.52
885.26
1449.09
1096.47
1348.67
861.07
1581.42
1010.88
1259.34
1019.24
1380.10
853.16
1179.06
763.90
1135.10
245.40
958
316.46
395.56
240.30
1238
351.22
646.26
914.16
595.61
760.72
904.96
1000.96
1425.66
0.0858
0.1232
0.0460
0.0671
0.0849
0.0571
0.0337
0.0704
0.1040
0.0321
0.0171
0.0279
0.0686
0.0574
0.0506
0.0568
0.1093
0.0696
0.0338
0.0678
0.0384

0.0293
0.0403
0.0233

0.0132
0.0264
0.0583
0.0503
0.0227
0.0517
0.0133
0.0218
86.33
85.85
48.40
46.65
94.18
40.00
38.07
48.58
94.85
23.80
19.86
17.64
67.86
45.58
49.64
41.16
128.11
59.03
44.25
59.73
156.48

92.59
101.88
96.96

37.58
40.85
63.77
84.45
29.84
57.13
13.29
15.29
-------
Sample Flow Correct
On
Date
PSAPCA
11-20
11-23
11-27
11-30
12-04
12-07
12-11
12-12
12-13
12-14
12-15
12-18

Time
(Alexl
1250
1234
1440
0027
2123
0755
2025
1505
1456
2110
1520
2210

Mag
R
Temp

Pres
M
Std
Off
Date
Time
Mag
R
Temp

Pres
M
Std
Mean
M Std
Cal.
Curve
Inter- Rate.at STP
cept
m /min
Total
Minutes
Vol ume
m*
Filter
Weight
g

TSP
ug/m
Duplicate:
50
50
50
50
50
48
50
50
50
50
50
50
509.58
503.58
513.58
499.58
505.58
499.58
487.58
496.58
501 . 58
493.58
499.58
497.58
29.90
29.60
30.29
30.25
29.94
29.98
30.37
30.31
30.27
30.24
30.20
29.99
7.25
7.26
7.27
7.37
7.29
7.19
7.47
7.40
7.36
7.41
7.36
7.35
11-23
11-27
11-30
12-04
12-07
12-11
12-12
12-13
12-14
12-15
12-18
12-21
1215
1430
0017
2042
0720
2016
1500
1453
2000
1515
1735
1715
48
40
18
40
0
12
44
46
50
48
0
40
503.58
513.58
499.58
505.58
499.58
487.58
496.58
501.58
493.58
499.58
497.58
502.58
29.60
30.29
30.25
29.94
29.98
30.37
30.31
30.27
30.24
30.20
29.99
30.23
7.11
6.50
4.42
6.52
0.00
3.66
6.94
7.06
7.41
7.21
0.00
6.57
7.18
6.88
5.85
6.94
3.64
5.42
7.21
7.23
7.38
7.31
3.68
6.96
35.9
35.9
35.9
35.9
29.8
29.8
29.8
29.8
29.8
29.8
29.8
30.4
-1.25
-1.25
-1.25
-1.25
-0.357
-0.357
-0.357
-0.357
-0.357
-0.357
-0.357
-0.552
0.235
0.227
0.198
0.228
0.134
0.194
0.254
0.254
0.260
0.257
0.136
0.247
4277
5918
4215
6162
3476
6502
1119
1428
1748
1081
4456
4009
1004.63
1340.66
833.14
1406.41
466.59
1261.31
284.12
363.45
454.08
278.22
603.89
990.54
0.0512
0.0621
0.1032
0.0696
0.0325
0.0740
0.0344
0.0276
0.0419
0.0257
0.0317
0.0643
50.96
46.32
123.87
49.49
69.65
58.67
121.07
75.94
92.28
92.37
52.49
64.91
Tvee Marina:
06-30
07-06
07-10
07-14
07-17
07-20
07-24
07-27
07-31
08-03
08-07
08-10
08-14
1810
1225
1400
1300
1230
1600
1645
1750
1445
1625
1355
1745
1305
50
50
49
49
50
50
50
50
50
50
50
50
50
513.58
530.58
524.58
521.58
529.58
524.58
536.58
532.58
523.58
532.58
536.58
531.58
529.58
29.87
30.10
29.96
30.10
30.02
30.04
30.02
30.05
29.87
30.46
30.44
30.45
30.49
7.22
7.13
7.08
7.12
7.13
7.17
7.08
7.11
7.15
7.16
7.13
7.17
7.18
07-06
07-10
07-14
07-17
07-20
07-24
07-27
07-31
08-03
08-07
08-10
08-14
08-17
1205
1345
1230
1125
1545
1615
1414
1435
1615
1345
1715
1255
1215
43
47
46
46
50
48
50
50
50
42
52
50
48
530.58
524.58
521.58
529.58
524.58
536.58
532.58
523.58
532.58
536.58
531.58
529 . 58
527.58
30.10
29.96
30.10
30.02
30.04
30.02
30.05
29.87
30.46
30.44
30.45
30.49
30.38
6.61
6.94
6.90
6.84
7.17
6.94
7.11
7.15
7.16
6.54
7.31
7.18
7.04
6.92
7.04
6.99
6.98
7.15
7.06
7.10
7.13
7.16
6.85
7.22
7.18
7.11
37.8
37.8
37.8
37.8
36.5
36.5
36.5
37.7
37.7
37.7
37.7
37.7
37.7
-2.11
-2.11
-2.11
-2.11
-1.97
-1.97
-1.97
-1.72
-1.72
-1.72
-1.72
-1.72
-1.72
0.239
0.242
0.241
0.240
0.250
0.247
0.248
0.235
0.235
0.227
0.237
0.236
0.234
8273
5840
4229
5634
4509
5775
4288
5568
4410
5597
4520
5472
4271
1975.23
1412.88
1018.09
1354.84
1126.63
1427.93
1064.95
1307.08
1038.16
1272.32
1071.85
1291.07
1000.34
0.0501
0.0284
0.0196
0.0244
0.0243
0.0202
0.0213
0.0313
0.0248
0.0242
0.0311
0.0296
0.0276
25.36
20.10
19.25
18.01
21.57
14.15
20.00
23.95
23.89
19.02
29.02
22.93
27.59
-------
to
oo
Sample Flow
On
Date
Tyee
08-17
08-21
08-24
08-28
09-01
09-05
09-07
09-11
09-14
09-18
09-21
09-25
09-28
10-02
10-05
10-09
10-12
10-16
10-19
10-23
10-26
10-30
11-02
11-06
11-09
11-13
11-16
11-20
11-23
11-27
11-30
12-04
Time
Marina.
1220
1330
1145
1235
1120
0000
1545
955
835
1516
2010
2035
900
1624
1450
2220
1615
2105
1700
1915
0905
1206
2215
2034
0845
1956
2156
1335
2045
1520
1245
1303
Mag
R
Temp

Pres
M
Std
Off
Date
Time
Mag
R
Temp

Pres
M
Std
Mean
M Std
Cal.
Curve
Inter- Rate,at STP
cept
m /min
Correct
Total
Minutes
Vol ume
m3
Filter
Weight
9

TSP
ug/m
cont'd:
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
527.58
529.58
519.58
523.58
519.58
521.58
537.58
523.58
517.58
526.58
525.58
518.58
515.58
521.58
522.58
516.58
517.58
509.58
513.58
509.58
507.58
503.58
498.58
504.58
514.58
504.58
501.58
511.58
502.58
510.58
798.58
515.58
30.38
30.15
30.54
30.48
30.35
30.03
29.89
30.48
30.41
30.42
30.46
30.37
30.54
30.53
30.49
30.62
30.42
30.57
29.93
29.56
29.80
30.21
30.18
29.73
29.99
29.95
30.03
29.89
29.67
30.29
30.20
29.79
7.19
7.14
7.26
7.22
7.24
7.15
7.12
7.22
7.26
7.20
7.21
7.25
7.29
7.24
7.23
7.29
7.26
7.33
7.23
7.21
7.26
7.33
7.37
7.27
7.23
7.30
7.33
7.24
7.28
7.29
5.82
7.20
08-21
08-24
08-28
09-01
09-05
09-07
09-11
09-14
09-18
09-21
09-25
09-28
10-02
10-05
10-09
10-12
10-16
10-19
10-23
10-26
10-30
11-02
11-06
11-09
11-13
11-16
11-20
11-23
11-27
11-30
12-04
12-07
1325
1100
1205
1110
1150
1535
945
830
1455
847
2019
835
1614
1441
2150
1610
2055
1650
1905
0900
1136
1005
2023
0840
1945
2141
1329
1255
1510
0100
1253
0820
48
48
48
46
54
47
46
46
46
45
59
48
46
42
44
49
42
41.
43"
50
44
38
48
49
48
38
44
0
48
12
42
48
529.58
519.58
523.58
519.58
521.58
537.58
523.58
517.58
526.58
525.58
518.58
515.58
521.58
522.58
516.58
517.58
509 . 58
513.58
509.58
507.58
503.58
498.58
504.58
514.58
504.58
501.58
511.58
502.58
510.58
798.58
515.58
499.58
30.15
30.54
30.48
30.35
30.03
29.89
30.48
30.41
30.42
30.46
30.37
30.54
30.53
30.49
30.62
30.42
30.57
30.32
29.56
29.80
30.21
30.18
29.73
29.99
29.95
30.03
29.89
29.67
30.29
30.20
29.79
29.96
7.00
7.11
7.08
6.94
7.53
7.20
6.93
6.96
6.90
6.84
7.87
7.14
6.95
6.63
6.84
7.19
6.72
6.59
6.69
7.26
6.88
6.42
7.12
7.16
7.15
6.39
6.79
0.00
7.15
2.85
6.60
7.18
7.10
7.13
7.17
7.08
7.39
7.18
7.03
7.09
7.08
7.02
7.54
7.20
7.12
6.94
7.04
7.24
6.99
6.96
6.96
7.23
7.07
6.88
7.24
7.21
7.19
6.84
7.06
3.62
7.21
5.07
6.21
7.19
37.7
37.7
37.7
37.7
37.7
37.7
37.7
37.7
37.7
38.7
38.7
38.7
38.7
38.7
38.7
38.7
34.4
34.4
34.4
34.4
34.4
36.7
36.7
36.7
36.7
. 36.7
36.7
36.7
35.2
35.2
35.2
35.2
-1.72
-1.72
-1.72
-1.72
-1.72
-1.72
-1.72
-1.72
-1.72
-2.41
-2.41
-2.41
-2.41
-2.41
-2.41
-2.41
-1.27
-1.27
-1.27
-1.27
-1.27
-1.89
-1.89
-1.89
-1.89
-1.89
-1.89
-1.89
-1.63
-1.63
-1.63
-1.63
0.234
0.235
0.236
0.233
0.242
0.236
0.232
0.234
0.233
0.244
0.257
0.248
0.246
0.241
0.244
0.249
0.240
0.239
0.239
0.247
0.242
0.239
0.249
0.248
0.247
0.238
0.244
0.150
0.251
0.190
0.223
0.251
5823
4170
5781
5677
5847
3093
5371
4232
6169
4587
5767
3598
6197
4217
6165
3929
6039
4043
5887
3700
5971
4918
5633
3603
6249
4423
5246
4280
5469
4229
5342
4036
1361.53
978.35
1363.21
1325.14
1412.12
729.77
1245.87
988.96
1439.98
1117.71
1482.73
892.99
1526.03
1018.29
1504.61
979.71
1450.06
967.26
1408.09
914.74
1447.27
1174.94
1401.92
893.59
1545.86
1052.35
1279.15
642.54
1373.49
805.41
1189.83
1011.49
0.0264
0.0230
0.0389
0.0339
0.0337
0.0296
0.0537
0.0542
0.0418
0.0540
0.0604
0.0354
0.0421
0.0510
0.0776
0.0331
0.0682
0.0803
0.0414
0.0315
0.0698
0.0776
0.0265
0.0258
0.0371
0.0657
0.0475
0.0435
0.0425
0.0997
0.0498
0.0461
19.39
23.51
28.54
25.58
23.86
40.56
43.10
54.80
29.03
48.31
40.74
39.64
27.59
50.08
51.57
33.79
47.03
83.02
29.40
34.44
48.23
66.05
18.90
28.87
24.00
62.43
37.13
67.70
30.94
123.79
41.85
45.58
-------
to
On
Date Time Mag
Tvee Marina, cont
12-07 0825 50
12-11 1550 50
12-11 PUF Plug
12-12 1535 50
12-13 1431 50
12-14 1605 50
12-14 PUF Plug
12-15 1550 50
12-16 1804 50
12-18 1830 50
12-21 1638 50
12-23 1340 50
12-25 1800 50
01-02 1725 50
01-05 1515 50
R
Temp
'd:
499.58
499.58

499.58
503.58
501.58

501.58
497.58
497.58
505.58
502.58
501.58
500.58
512.58

Pres

29.96
30.40

30.31
30.27
30.25

30.20
29.97
29.99
30.23
30.43
30.26
30.13
29.84
M
Std

7.33
7.39

7.38
7.34
7.35

7.35
7.35
7.35
7.32
7.37
7.36
7.35
7.233
Off
Date

12-11
12-12
12-14
12-13
12-14
12-15
12-18
12-16
12-18
12-21
12-23
12-25
12-28
01-05
01-09
Time Mag

1532 34
1530 44

1426 48
1530 44
1545 48

1756 49
1820 48
1628 44
1335 43
1745 51
1410 45
1505 46
1640 52
R
Temp

499.58
499.58

503.58
501.58
501.58

497.58
497 . 58
505.58
502.58
501.58
502,58
512.58
505.58

Pres

30.40
30.31

30.27
30.25
30.20

29.97
29.99
30.23
30.43
30.26
30.26
29.84
29.72
M
Std

6.09
6.92

7.19
6.90
7.20

7.28
7.20
6.87
6.83
7.43
6.97
6.93
7.40
Mean
M Std

6.71
7.15

7.28
7.12
7.28

7.31
7.28
7.11
7.08
7.40
7.16
7.14
7.31
Cal.
Curve

35.2
38.0

38.0
38.0
38.0

38.0
38.0
38.0
38.0
38.0
38.0
28.5
28.5
Inter-
cept

-1.63
-2.28

-2.28
-2.28
-2.28

-2.28
-2.28
-2.28
-2.28
-2.28
-2.28
0.0256
0.0256
Tvee Marina Duplicate:
07-20 1600 50
07-24 1615 50
07-27 1805 50
07-31 1500 50
08-03 1635 50
08-07 1405 50
08-10 2310 50
08-14 1315 50
08-17 0030 50
08-21 1340 50
524.58
536.58
532.58
523.58
532.58
536.58
531.58
529.58
527.58
529.58
30.04
30.02
30.05
29.87
30.46
30.44
30.45
30.49
30.38
30.15
7.17
7.08
7.11
7.15
7.16
7.13
7.17
7.18
7.19
7.14
07-24
07-27
07-31
08-03
08-07
08-10
08-14
08-17
08-21
08-24
1645 50
1655 47
1450 45
1630 50
1355 47
1740 50
1305 44
1220 50
1335 49
1100 50
536.58
532.58
523 . 58
532.58
536.58
531.58
529.58
527.58
529 . 58
519.58
30.02
30.05
29.87
30.46
30.44
30.45
30.49
30.38
30.15
30.54
7.08
6.90
6.78
7.16
6.91
7.17
6.74
7.19
7.07
7.26
7.13
6.99
6.95
7.16
7.04
7.15
6.96
7.19
7.13
7.20
40.6
40.6
35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.3
-2.97
-2.97
-1.25
-1.25
-1.25
-1.25
-1.25
-1.25
-1.25
-1.25
                                                                                                              Sample Flow
                                                                                                      Inter-   Rate at STP   Total
                                                                                                                 m /min
                                                                                                                  0.237
                                                                                                                  0.248

                                                                                                                  0.252
                                                                                                                  0.247
                                                                                                                  0.251

                                                                                                                  0.252
                                                                                                                  0.251
                                                                                                                  0.247
                                                                                                                  0.246
                                                                                                                  0.255
                                                                                                                  0.248
                                                                                                                  0.250
                                                                                                                  0.256
                                                                                                                 0.249
                                                                                                                 0.245
                                                                                                                 0.232
                                                                                                                 0.238
                                                                                                                 0.235
                                                                                                                 0.238
                                                                                                                 0.232
                                                                                                                 0.239
                                                                                                                 0.237
                                                                                                                 0.239

Total
Minutes
6187
1405

1373
1497
1415

1572
2894
4199
2706
3124
4092
4183
5571
5175
4327
5562
4409
5601
4542
5155
4269
5825
4163
Correct
Vol yme
m3
1466.26
348.77
1065
345.63
370.41
355.83
1480
396.71
727.72
1037.67
666.27
795.66
1016.75
1043.84
1424.87
1286.74
1061.50
1291.23
1049.79
1314.57
1080.82
1198.21
1020.09
1382.82
996.53
Filter
Weight
9
0.0681
0.0452

0.0154
0.0361
0.0297

0.0141
0.0242
0.0518
0.0468
0.0233
0.0550
0.0209
0.0359
0.0198
0.0227
0.0333
0.0250
0.0259
0.0318
0.0265
0.0254
0.0254
0.0216

TSP
ug/m
46.44
129.60

44.56
97.46
83.47

35.54
33.25
49.92
70.24
29.28
54.09
20.02
25.20
15.39
21.38
25.79
23.81
19.70
29.42
22.12
24.90
18.37
21.68
-------
Sample Flow
On
Date
Brown'
07-10
07-13
07-17
08-24
08-28
09-01
09-05
09-07
09-11
09-14
09-18
09-21
09-25
09-28
10-02
10-05
10-23
10-26
10-30
11-02
11-06
11-09
11-13
11-16

Time

Mag
R
Temp

Pres
M
Std
Off
Date
Time
Mag
R
Temp

Pres
M
Std
Mean
M Std
Cal.
Curve
Inter- Rateoat STP
cept
m /min
Total
Minutes
Correct
Vol ume
m3
Filter
Weight
g

TSP
ug/m
s Point:
1310
1150
1425
1300
1315
1050
1230
1645
1020
900
1600
1922
1957
820
1650
1540
1805
0930
1110
1105
2107
0905
2054
2242
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
50
522.58
524.58
533.58
519.58
523.58
519.58
521.58
537.58
523.58
517.58
527.58
525.58
518.58
515.58
521.58
521.58
509.58
507.58
503 . 58
498.58
504.58
514.58
504.58
501.58
29.96
30.1
30.02
30.54
30.48
30.35
30.03
29.89
30.48
30.41
30.42
30.46
30.37
30.54
30.53
30.49
29.56
29.80
30.21
30.25
29.73
30.00
29.98
30.03
7.17
7.17
7.10
7.26
7.22
7.24
7.16
7.12
7.22
7.26
7.19
7.21
7.25
7.29
7.24
7.24
7.21
7.26
7.33
7.38
7.27
7.23
7.30
7.33
07-13
07-17
07-20
08-28
09-01
09-05
09-07
09-11
09-14
09-18
09-21
09-25
09-28
10-02
10-05
10-09
10-26
10-30
11-02
11-06
11-09
11-13
11-16
11-20
1135
1315
1230
1305
1025
1215
1635
1015
850
1549
1854
1943
815
1642
1533
2340
0920
1104
2250
2056
0900
2020
2227
1239
42
49
50
45
50
54
47
52
48
46
48
45
49
48
45
44
52
47
38
48
50
49
43
46
524.58
533.58
532.58
523.58
519.58
521.58
537.58
523.58
517.58
527.58
525.58
518.58
515.58
521.58
521.58
516.58
507.58
503.58
498.58
504.58
514.58
504.58
501.58
509.58
30.1
30.02
29.58
30.48
30.35
30.03
29.89
30.48
30.41
30.42
30.46
30.37
30.54
30.53
30.49
29.49
29.80
30.21
30.25
29.73
30.00
29.98
30.03
29.90
6.57
7.03
7.11
6.85
7.24
7.20
7.53
7.37
7.04
6.90
7.06
6.87
7.21
7.10
6.87
6.84
7.40
7.11
6.43
7.12
7.23
7.23
6.79
6.96
6.87
7.10
7.11
7.06
7.23
7.22
7.35
7.25
7.13
7.08
7.13
7.04
7.23
7.20
7.06
7.04
7.31
7.18
6.88
7.25
7.25
7.23
7.05
7.14
35.5
35.5
40.6
35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.5
35.5
35.5
35.5
35.5
35.5
35.5
35.5
35.5
35.5
35.5
32.7
32.7
-1.65
-1.65
-2.97
-1.25
-1.25
-1.25
-1.25
-1.25
-1.25
-1.25
-1.25
-1.81
-1.81
-1.81
-1.81
-1.81
1.81
1.81
1.81
1.81
1.81
1.81
-0.987
-0.987
0.240
0.246
0.248
0.235
0.240
0.240
0.243
0.241
0.237
0.236
0.237
0.249
0.255
0.254
0.250
0.249
0.257
0.253
0.245
0.255
0.255
0.255
0.246
0.249
4221
5855
4208
5764
5589
5847
3129
5370
4232
6169
4498
5783
3611
6263
4242
6236
3785
5913
5017
5640
3594
6431
4425
4841
1013.04
1443.13
1044.23
1356.09
1342.63
1402.95
761.86
1292.30
1004.65
1455.74
1067.16
1441.68
919.53
1588.68
1059.31
1554.61
972.75
1495.99
1229.17
1438.20
916.47
1639.91
1087.05
1203.57
0.0171
0.0240
0.0210
0.0366
0.0293
0.0381
0.0266
0.0692
0.0551
0.0406
0.0483
0.0661
0.0311
0.0387
0.0581
0.0753
0.0299
0.0643
0.0728

0.0161
0.0352
0.0514
0.0443
16.88
16.63
20.11
26.99
21.82
27.16
34.91
53.55
54.84
27.89
45.26
45.85
33.82
24.36
54.85
48.44
30.74
42.98
59.22,
(a
17.57
21.47
47.28
36.81
-------
Sample Flow
On
Date

Time

Mag
R
Temp

Pres
M
Std
Off
Date
Time
Mag
R
Temp

Pres
M
Std
Mean
M Std
Cal.
Curve
Inter- Rate.at STP
cept
3, .
m /mm
Total
Minutes
Correct
Volume
mS
Filter
Weight
g

TSP
ug/m
Seal and:
07-20
07-24
07-27
07-31
08-03
08-07
08-10
08-14
08-17
08-21
11-16
11-20
11-27
11-30
12-04
12-07
12-11
12-11
12-12
12-13
12-14
12-14
12-15
12-18
01-02
1715
1255
1415
1350
1441
1230
1630
1220
1150
1300
1645
1230
1343
0950
1150
1005
1515
PUF
1450
1406
1500
PUF
1505
1355
1645
50
50
50
50
50
50
49
50
50
50
50
42
56
50
50
50
50
Plug
50
50
50
Plug
50
50
50
527.58
534.58
532.58
523.58
534.58
539.58
535.58
530.58
529.58
533.58
509.58
512.58
511.58
494.58
517.58
507.58
500.58

500.58
506.58
503 . 58

503.58
505.58
500.58
30.04
30.02
30.05
29.87
30.46
30.44
30.45
30.49
30.38
30.15
30.08
29.90
30.29
30.20
29.78
29.96
30.41

30.31
30.27
30.25

30.19
29.95
30.13
7.15
7.10
7.11
7.15
7.15
7.11
7.07
7.18
7.17
7.12
7.28
6.63
7.71
7.40
7.18
7.28
7.38

7.37
7.32
7.34

7.33
7.29
7.35
07-24
07-27
07-31
08-03
08-07
08-10
08-14
08-17
08-21
08-24
11-20
11-27
11-30
12-04
12-07
12-11
12-12
12-14
12-13
12-14
12-15
12-18
12-18
12-21
01-05
315
1330
1250
1434
1215
1625
1155
1145
1350
935
1220
1333
0930
1135
0845
1505
1445

1401
1430
1500

1345
1606
1600
45
48
50
51
48
47
46
49
45
49
42
44
2
11
0
40
46

48
48
46

48
45
44
534.58
532.58
523.58
534.58
539.58
535.58
530.58
529.58
533 . 58
519.58
512.58
511.58
494.58
517.58
507.58
500.58
500.58

506.58
503.58
503.58

505.58
507.58
512.58
30.02
30.05
29.87
30.46
30.44
30.45
30.49
30.38
30.15
30.54
29.90
30.29
30.20
29.78
29.96
30.41
30.31

30.27
30.25
30.19

29.95
30.23
29.85
6.73
6.97
7.15
7.22
6.97
6.92
6.89
7.10
6.75
7.19
6.63
6.84
1.48
3.37
0.00
6.60
7.07

7.17
7.19
7.03

7.14
6.93
6.78
6.94
7.04
7.13
7.19
7.06
7.02
6.98
7.14
6.96
7.16
6.95
6.73
4.60
5.38
3.59
6.94
7.22

7.27
7.26
7.19

7.24
7.11
7.06
36.3
36.3
36.3
36.3
36.3
36.3
36.3
36.3
36.3
36.3
34.5
27.8
27.8
27.8
27.8
27.8
27.8

27.8
27.8
27.8

27.8
27.8
27.8
-1.52
-1.52
-1.52
-1.52
-1.52
-1.52
-1.52
-1.52
-1.52
-1.52
-0.99
0.358
0.358
0.358
0.358
0.358
0.358

0.358
0.358
0.358

0.358
0.358
0.358
0.233
0.236
0.238
0.240
0.236
0.235
0.234
0.239
0.234
0.239
0.230
0.229
0.152
0.181
0.116
0.237
0.247

0.249
0.248
0.246

0.247
0.243
0.241
4814
4356
5019
4360
5613
4536
5483
4284
5819
4155
5492
10124
4072
5866
4120
3851
1414

1393
1465
1440

4240
4451
4570
1121.94
1026.60
1195.99
1045.56
1326.71
1066.52
1283.90
1022.02
1359.37
992.96
1264.29
2321.24
620.70
1060.50
479.20
911.46
349.31
1063
346.23
363.45
353.58
1402
1049.07
1081.23
1102.25
0.0696
0.0732
0.0480
0.0526
0.0436
0.0637
0.0659
0.0535
0.0540
0.0361
0.0604
0.0690
0.1007
0.1052
0.0748
0.0738
0.0576

0.0509
0.0404
0.0326

0.0507
0.0657
0.0282
62.04
71.30
40.13
50.31
32.86
59.73
51.33
52.35
39.72
36.36
47.77
29.73
162.24
99.20
156.09
80.97
164.90

147.01
111.16
92.20

48.33
60.76
25.68
-------
On
Date
Morse
07-20
07-24
07-27
07-31
08-03
08-07
08-10
08-14
08-17
08-21
11-16
11-20
11-27
to 11-30
10 12-04
12-07
12-11
12-11
12-12
12-13
12-14
12-14
12-15
12-18
01-02
01-05
Time Mag
Supply:
1645 50
1330 50
1445 50
1230 50
1550 50
1310 50
1610 50
1140 50
1125 50
1235 50
1445 50
1210 50
1420 50
0910 50
1226 50
0940 50
1445 50
PUF Plug
1555 50
1350 50
1345 50
PUF Plug
1610 50
1415 50
1625 50
1550 50
R
Temp

532.58
533.58
531.58
523.58
533.58
537.58
535.58
530.58
529.58
533.58
509.58
512.58
512.58
497.58
517.58
507.58
499.58

500.58
506.58
497.58

501.58
505.58
500.58
512.58

Pres

30.04
30.02
30.05
29.87
30.46
30.44
30.45
30.49
30.38
30.15
30.12
29.60
30.29
29.19
29.79
29.96
30.41

30.31
30.27
30.25

30.20
29.95
30.13
29.85
M
Std

7.11
7.10
7.12
7.15
7.15
7.13
7.14
7.18
7.17
7.12
7.28
7.20
7.28
7.25
7.18
7.28
7.39

7.37
7.32
7.38

7.35
7.29
7.35
7.23
Off
Date

07-24
07-27
07-31
08-03
08-07
08-10
08-14
08-17
08-21
08-24
11-20
11-27
11-30
12-04
12-07
12-11
12-12
12-14
12-13
12-14
12-15
12-18
12-18
12-21
01-05
01-09
Time

1315
1430
1215
1450
1250
1605
1135
1120
1220
910
1201
1310
0900
1216
0915
1444
1550

1343
1335
1605

1405
1552
1540
1445
Mag

43
50
50
46
46
48
49
48
46
50
40
40
0
8
49
24
46

45
49
46

45
44
48
48
R
Temp

533.58
531.58
523.58
533.58
537.58
535.58
530.58
529.58
533.58
519.58
512.58
512.58
497.58
517.58
507.58
499.58
500.58

506.58
497.58
501.58

505.58
507.58
512.58
505.58

Pres

30.02
30.05
29.87
30.46
30.44
30.45
30.49
30.38
30.15
30.54
29.60
30.29
29.19
29.79
29.96
30.41
30.31

30.27
30.25
30.20

29.95
30.23
29.85
29.63
M
Std

6.59
7.12
7.15
6.86
6.82
6.99
7.11
7.03
6.83
7.26
6.44
6.51
0.00
2.87
7.20
5.12
7.07

6.94
7.31
7.05

6.91
6.86
7.08
7.10
Mean
M Std

6.85
7.11
7.14
7.01
6.99
7.06
7.13
7.11
7.00
7.19
6.86
6.85
3.64
5.06
7.19
6.20
7.23

7.16
7.31
7.22

7.13
7.07
7.21
7.16
Cal.
Curve

37.8
37.8
37.8
37.8
37.8
37.8
37.8
37.8
37.8
37.8
32.2
32.2
32.2
32.2
32.2
32.2
32.2

32.2
32.2
32.2

32.2
32.2
32.2
32.2
Inter-
cept

-2.17
-2.17
-2.17
-2.17
-2.17
-2.17
-2.17
-2.17
-2.17
-2.17
-0.768
-0.768
-0.768
-0.768
-0.768
-0.768
-0.768

-0,768
-0.768
-0.768

-0.768
-0.768
-0.768
-0.768
Sample Flow
Rate at STP
m /min
0.239
0.246
0.246
0.243
0.242
0.244
0.246
0.245
0.243
0.248
0.237
0.237
0.137
0.181
0.247
0.216
0.248

0.246
0.251
0.248

0.245
0.243
0.248
0.247

Total
Minutes
5546-
4224
5773
4460
5581
2936
5430
4297
5876
4113
5597
10128
4070
5947
4131
6070
1499

1309
1425
1577

4199
4414
4273
5701
Correct
Volume
m3
1323.41
1037.00
1421.10
1082.55
1351.69
716.91
1335.23
1054.36
1425.47
1018.46
1325.54
2397.28
557.05
1076.93
1021.31
1312.96
372.23
1052
322.04
357.59
390.90
1421
1030.11
1074.74
1061.35
1408.15
Filter
Weight
g
0.0532
0.0546
0.0555
0.0390
0.0403
0.0381
0.0542
0.0593
0.0632
0.0269
0.0643
0.0762
0.0918
0.1023
0.0421
0.0682
0.0565

0.0242
0.0398
0.0400

0.0428
0.0682
0.0262
0.0258

TSP3
ug/m
40.20
52.65
39.05
36.03
29.81
53.14
40.59
56.24
44.34
26.41
48.51
31.79
164.80
94.99
41.22
51.94
151.79

75.15
111.30
102.33

41.55
63.46
24.69
18.32
-------
Sample Flow
On R M
Date Time Mag Temp Pres Std
Riverside School :
07-20 1440 50 529.58 30.04 7.13
07-24 1410 50 535.58 30.02 7.09
07-27 1200 50 528.58 30.05 7.14
07-31 1150 50 525.58 29.87 7.14
08-03 1420 50 536.58 30.46 7.13
08-07 1530 50 541.58 30.44 7.10
08-10 1545 50 532.58 30.45 7.16
08-14 1115 50 523.58 30.49 7.23
08-17 1055 50 533.58 30.38 7.21
08-21 1140 50 527.58 30.15 7.16
11-16 1600 50 499.58 30.10 7.35
11-20 1142 50 509.58 29.89 7.25
11-23 2142 50 498.58 29.67 7.30
11-27 1253 50 514.58 30.28 7.26
11-30 0815 50 481.58 30.17 7.50
12-04 2220 50 502.58 29.97 7.31
12-07 1035 50 501.58 29.96 7.32
12-11 1423 50 499.58 30.41 7.39
12-11 PUF Plug
12-12 1620 50 487.58 30.31 7.47
12-13 1520 50 502.58 30.28 7.35
12-14 PUF Plug
12-14 0830 50 479.58 30.28 7.52
12-15 1635 50 492.58 30.20 7.41
12-18 1915 50 497.58 29.99 7.35
01-02 1840 50 491.58 30.13 7.41
01-05 1715 50 512.58 29.88 7.23
(a) - Filter weight missing
Off

Date Time Mag

07-24
07-27
07-31
08-03
08-07
08-10
08-14
08-17
08-21
08-24
11-20
11-23
11-27
11-30
12-04
12-07
12-11
12-12
12-14
12-13
12-14
12-18
12-15
12-18
12-21
01-05
01-09

(b) - Power went out, so end time is calculated
(c) - Motor stopped; meter continued to
(d) - PS-1 was turned off approximately
operate

1400 49
1740 50
1135 47
1335 49
1520 46
1530 47
1105 47
1045 46
1110 47
840 51
1135 50
2130 50
1243 46
0800 0
2202 2
1030 45
1415 45
1615 48

1516 47
0820 44

1630 48
1905 49
1532 46
1705 48
2005 55

based on

210 minutes after
R
Temp

535.58
528.58
525.58
536.58
541.58
532.58
523.58
533.58
527.58
511.58
509 . 58
498.58
514.58
481 . 58
502.58
501 . 58
499.58
487.58

502.58
479.58

492.58
497.58
507.58
512.58
499.58


Pres

30.02
30.05
29.87
30.46
30.44
30.45
30.49
30.38
30.15
30.54
29.89
29.67
30.28
30.17
29.97
29.96
30.41
30.31

30.28
30.28

30.20
29.99
30.23
29.88
29.84

M
Std

7.02
7.14
6.92
7.06
6.81
6.94
7.01
6.92
6.94
7.39
7.25
7.30
6.97
0.00
1.46
6.94
7.01
7.32

7.13
7.06

7.26
7.28
7.01
7.08
7.68

Mean
M Std

7.08
7.12
7.03
7.10
6.97
7.02
7.09
7.08
7.08
7.28
7.30
7.28
7.14
3.63
4.48
7.13
7.16
7.35

7.30
7.20

7.39
7.35
7.18
7.25
7.45

Cal.
Curve

35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.3
35.3
37
37
37

37
37

37
37
37
37
37

Inter- Rate.at STP
cept

-0.947
-0.947
-0.947
-0.947
-0.947
-0.947
-0.947
-0.947
-0.947
-0.947
-0.947
-0.947
-0.947
-0.947
-0.947
-1.78
-1.78
-1.78

-1.78
-1.78

-1.78
-1.78
-1.78
-1.78
-1.78

•j
m /min

0.227
0.228
0.226
0.228
0.224
0.226
0.228
0.227
0.227
0.233
0.234
0.233
0.229
0.130
0.154
0.241
0.242
0.247

0.245
0.243

0.248
0.247
0.242
0.244
0.250

Total
Minutes

5709
210
5681
4425
5820
4316
5475
4292
5774
4141
5491
4913
5516
3731
6590
3601
5981
1546

1379
1016

1919
4474
4095
4223
5933

Correct
Volume
m3

1297.38
47.96
1283.78
1008.72
1305.30
974.10
1245.76
975.37
1312.15
964.51
1283.07
1144.80
1262.98
484.01
1012.88
866.81
1445.81
381.50
966
337.86
246.75
1579
475.74
1103.42
991.66
1030.51
1480.44

Filter
Weight
g

0.0414
0.0051
0.0444
0.0201
0.0551
0.0419
0.0443
0.0443
0.0447
0.0233
0.0682
0.0371
0.0202
0.0842
0.0737
0.0253
0.0556
0.0478

0.0209
0.0128

0.0244
0.0324
0.0373
0.0152
0.0153


TSP
ug/m

31.91...
106.34(d)
34.59
19.93
42.21
43.01
35.56
45.42
34.07
24.16
53.15
32.41
15.99
173.96
72.76
29.19
38.46
125.29

61.85
51.87

51.29
29.36
37.61
14.75
16.99

the meter

filter










was begun
-------
Appendix C-4.  Elemental Aerosol Concentrations
                                         135
-------
PSWQA AIR SAMPLING
Elemental Aerosol Concentrations at Six Tacoma Sites (ng/m3)
Element
S
Cl
K
Ca
Ti
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
Element
S
Cl
K
Ca
Tl
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
SL890727
804
115
161
897
67.3
7.61
5.14
21.1
861
5.92
109. .
0.00(3)
35.9
6.84
2.04
MS890727
674
87.7
196
570
68.9
3.18
6.24
24.4
816
3.96
40.6
11. 8
3.22
2.49
SL890814
957
176
206
907
98.2
7.32
10.0
38.5
1505
9.31
125
1.65
54.1
5.62
2.38
MS890814
894
241
253
1368
80.3, .
2.70(3)
7.31
38.2
1287
6.54
63.1
1.32
19.2
1.65
2.20
SL890821
763
296
204
857
61.4
7.36
5.02
23.7
796
6.66
63.8
0.41
26.5
2.39 •
13.4
MS890821
545
273
182
314
44.4.
1.88(3)
6.84
19.5
563
3.53
36.7
0.51
8.77
2.34
2.17
SL891116
2473
360
307
582
61.2
10.2
7.62
37.9
974
10.0
120. .
0.37(3J
76.1
4.91
6.47
MS891116
2987
841
267
1253
33.8
12.9
6.43
33.2
619
13.9
82.3
0.48
64.8
4.16
8.53
SL891211
4853
948
789
1658
220. .
13.0(3)
6.15
95.6
2903
19.1
233. .
1 1.16(3)
117
13.3
19.6
MS891211
4865
1078
808
1710
202.
12.3(3)
21.2
126
3356
26.5
242
1.09(3)
129
10.1
22.6
















MS891215
2162
279
238
590
76.8
5.46
3.43
31.4
915
6.70
78.6. .
0.39(3)
37.8
2.25
4.96
                                        137
-------
Element
S
Cl
K
Ca
Tl
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
Element
S
Cl
K
Ca
Tl
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
RS890727 RS890814 RS890821 RS891116
864 830 633 1193
79.0 128 209 278
252 310 133 190
558 724 -178 93.9
71.4 112 26.6 21.4
4.74 3.15 3.01 4.07
4.97 4.10 3.13 4.02
21.9 26.7 13.4 29.0
77.6 1047 342 350
4.79 3.68 2.76 4.25
30.0. . 24.7 25.2. . 64.7. .
0.05(a) 0.48 0.00(a) 0.36(3)
14.4 13.3 10.9. . 47.0
2.2 1.43 0.42(a) 5.02
2.7 2.85 1.80 7.82
DTM890727 DTM890814 DTM890821
706 610 671
168 155 405
100 145 105
335 374 511
39.2. 41.1 18.2
1.48(a) 3.47 4.30
2.33 3.41 3.03
12.8 14.9 13.1
419 403 366. .
3.19 3.86 2.39(a)
34.5. 22.8 23.0. .
0.00(3) 1.87 0.06(3)
9.74 10.9. . 10.6. .
0.81 0.45(a) 0.4l(3)
2.65 3.18 2.68
RS891127
3307
877
784
969
127.5
31.2
35.5
94.4
2092
41.1
161.7, ,
0.96(3)
151
10.5
28.4













RS891211
2159
404
386
196
53.1
9.58
-2.74 -1
59.0
1103
11.3
148. .
1.06(3)
101
4.41
17.2













RS891215
1025
98
113
181
36.6. .
3.3l(a)
.10
14.7
389
1.10
53.0.
0.37(a)
29.2
1.16
4.26













138
-------
Element
S
Cl
K
Ca
Ti
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
Element
S
Cl
K
Ca
Ti
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
TM890727
811
172
119
352
42.9
4.53
2.22
14.7
440
2.88
31.0
0.31
8.48
1.29
2.62
TM891116
1954
596
165
647
24.5
10.3
7.53
23.9
451
14.1
70.0,
0.36(a
41.4
3.17
7.48
TM890814
825
190
144
345
33.9
3.42
3.48
14.6
396
4.18
27.0
1.22
10.9, .
0.00(3)
3.13
TM891211
6249
3895
467
1944
136
26.4
6.98
108
2825
36.9
267
77.0
6.32
17.4
TM890821
816
509
108
512
23.0
4.68
3.97
11.6
346
2.43
29.0
0.41
6.99
1.18
2.49
TM891215
2076
548
110
481
43.6, .
7.75 a
5.12(a)
27.5
891
3.22
79.8, .
1.02(3)
32.7
2.92
6.58
TM890828
2154
308
180
399
43.8
6.61
1.05
12.0
424
3.81
28.7
1.14
11.2
1.23
4.11
TM891216
1793
536
135
554
36.5
8.21
-1.20(b
17.5
576
7.89
62.2
0.64
. 24.7,
1O O 1 u
C.O
4.22
TM890911
3044
431
346
1393
105
14.9
0.59
50.2
1421
13.9
104, .
0.47(3)
31.9
5.86
7.33






\
)





'

139
-------
Element
S
Cl
K
Ca
Ti
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
BP890828
708
241
104
181
24.2
4.23
0.09
8.42
273
1.68
15.1
0.78
7.80
1.77
4.53
BP890911
3174
355
350
1388
94.9
17.7
2.25
43.5
1248
15.3
62.9
1.21
34.4
6.12
9.06
BP891109
174
288
18.4
38.3
0.51
0.98
0.28
1.21
18.1
0.64
3.09

l!?l
0.17
1.40
Element
S
Cl
K
Ca
Ti
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
AS890724
1483
171
200
882
95.5
7.12
9.77
37.4
1463
9.05
122
1.60
52.6
5.46
2.32
AS890727
1311
181
261
1664
95.8
9.00
7.02
28.0
1170
5.89
45
0.40
17.7
3.28
2.43
AS890803
1062
283
328
1875
140
9.13
6.01
30.6
1488
6.50
42
0.94
12.2
1.78
2.76
AS890814
3080
531
395
3258
139
8.65
7.67
45.0
1808
7.12
63
1.70
21.3
3.83
3.72
AS890817
1567
81
250
1821
91.9
7.22
4.12
25.9
1173
4.64
32
0.77
13.0
2.49
1.98
AS890821
1640
374
184
2127
57.1
4.26
3.04
24.3
827
3.53
38
0.30
9.00
1.70
2.13
140
-------
Element
S
Cl
K
Ca
Ti
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
AS890828
. 352
583
452
2442
140
17.1
4.01
39.4
2881
8.54
53.9
0.84
22.0
3.66
5.15
AS890907
2451
400
566
2206
153
15.8
2.75
50.4
1719
13.8
72.9
0.50
32.7
2.98
4.44
AS890911
6736
548
816
6029
246
24.7
12.38
103
3930
29.6
221
0.58
76.8
50.3
10.05
AS890914
4835
1072
463
3938
121
10.9
3.34
42.5
1405
9.48
63.6
0.85
28.0
20.8
6.27
AS890918
3516
228
580
3003
181
10.3
4.41
67.2
2168
11.8
83.2
0.74
44.4
3.51
7.22
AS891102
942
629
132
310
35.0
6.62. .
-0.77(c)
12.5
439
3.01
20.0, .
0.30(a)
12.3
1.42
4.64
Element
S
Cl
K
Ca
Ti
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
AS891106
822
1148
99.0
244
19.2
-1 .19(c)
2.36
8.56
362
2.16
13.3. .
0.40(3)
6.77.
0.8l(3)
2.63
AS891109
880
420
104
187
13.1
5.03
0.22
11.1
235
2.75
34.9
13.4
2.27
3.38
AS891113
2128
1449
358
1145
106
7.24
11.0
46.3
1470
12.1
. 89.7. ,
) 0.46(3,
40.6
5.5
10.1
AS891116
2386
380
223
970
33.7
10.1
2.81
23.3
523
8.02
. 62.3. .
> 0.37(3)
45.3
3.50
7.60
AS891127
4882
1002
692
2383
187
40.0
15.9
97.9
2898
35.7
166
0.68
86.5
8.43
17.5
AS891130
2676
780
333
1227
90.6
19.0
9.1
48.7
1344
25.4
81.7, ,
0.4(3)
51.1
4.3
9.3
141
-------
Element    AS891204    AS891207    AS891211   AS891212   AS891213   AS891215
s
Cl
K
Ca
Ti
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
1701
1392
87.3
317
36.3
2\51
23.2
11.9
6.53
141
19.6
2.73
4.86
2105
937
241
526
49.8
13.1
6.08
37.8
984
16.3
86.3
0.51
43.1
6.03
8.69
5271
817
577
675
123
18.2
8.74
85.3
1873
33.09
292
1.89
102
8.51
22.2
3359
1193
505
1790
188. .
12(3)
14.1
88.8
2284
15.8
196
8K5.
3.3(3)
21.1
3475
1020
469
1217
162
15.7
6.01
83.3
2344
22.43
171. .
1.03(3)
69.3
5.28
14.1
1900
249
188
/i \
-6.12 b
9.25 a
-3.80(c)
26.8
584
6.11
77.0. .
1.16(3)
35.1. .
2.48(3)
9.6
Element    AS891216    AS891218
S
Cl
K
Ca
Ti
V
Cr
Mn
Fe
Ni
Zn
Se
Pb
As
Br
2056
436
246
571
60.9
6.20(3)
4.13
26.6
805
7.99
84.1.
0.63(3)
33.7
2.24
5.30
3446
519
351
1482
101
15.2
2.22
49.3
1442
15.5
89.4.
0.5l(3)
43.7
4.38
12.8
(a)  Metal was not detected  in sample; detection limit was  incorporated  into
     the calculations  in order to obtain an estimated value.

(b)  A negative number resulted when the background element value was
     subtracted from a smaller value detected  in the filter.

(c) Both (a) and  (b) apply.
                                      142
-------
Appendix C-5. Particulate PAH Concentrations
                                      143
-------
PSWQA  AIR SAMPLING
Particulate PAH Concentrations  at  Five Tacoma Sites (ng/m-*)
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a) anthracene
Crysene
Benzo (b)fl uoranthene
Benzo (k)fl uoranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Dibenzo (a, h) anthracene
Benzo (g , h , i ) peryl ene
TOTAL CPAH
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k) f 1 uoranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Dibenzo (a, h) anthracene
Benzo (g,h,i)perylene
TOTAL CPAH
AS0724
ND
ND
ND
ND
ND
0.351
ND
0.513
0.432.
0.27(a)
0.756
1.661
ND
0.432
0.635
ND
0.891
5.59
AS0814
ND
ND
ND
ND
ND
0.836. .
O.ll(a)
1.507
1.133. .
0.55(3)
1.133
1.892
ND
0.693
0.693
0.759
8.47
AS0727
0.07(b)
ND
ND
0.013
ND
0.098
ND
0.164
0.138. .
0.13(3)
0.321
0.577
ND
0.157
0.164.
0.07(3)
0.243
1.96
AS0821
ND
ND
ND
ND
ND
0.320
ND
0.552
0.463. .
0.36(3)
0.641
0.694
0.570
0.409
0.552
ND
0.605
4.84
AS0727
0.07(3)
ND
ND
ND
ND
0.171
ND
0.302
0.269
0.197
0.656
1.036
ND
0.26(3)
0.295
ND
0.374
3.39
AS0828
ND
ND
ND
ND
ND
ND
ND
0.90 a
0.77(3)
ND . .
0.97 a
0.96 a
0.42(3)
ND
0.36(3)
ND
0.56(3)
4.94
AS0803
ND
ND
ND
ND
ND
1.010
0.135
1.957
1.299
0.325
0.577
0.397. .
O.is'3/
0.198
0.207
ND
0.280
5.42
AS0907
ND
ND
ND
ND
ND
1.4
ND
5.7
4.3
1.9
7.1
4.9
2.0
1.1
1.1
0.40
1.4
29.9
                                         145
-------
PSWQA  AIR SAMPLING
Particulate PAH Concentrations at Five Tacoma Sites (ng/rn^)
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a) anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k)fl uoranthene
Benzo(a)pyrene
Indeno(l,2(3-c,d)pyrene
Dibenzo (a, h) anthracene
Benzo(g,h,i)perylene
TOTAL CPAH
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anthracene
Crysene
Benzo (b)fl uoranthene
Benzo (k)fl uoranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Dibenzo (a ,h) anthracene
Benzo (g,h, i)perylene
TOTAL CPAH
AS0911
ND
ND
ND
ND
ND
1.4(3)
ND
4.0
3.2
2.0
8.1
10(3)
ND
1 .4(a'
1.7.
0.60(3)
2.3
33.3
AS1106
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1 .o(3)
ND
ND
ND
ND
ND
1.0
AS0914
ND
ND
ND
ND
ND
ND
ND
0.89(3)
0.75(3)
ND
2.0
2.3
1.2
0.75
0.82.
0.68 a
1.2(3)
10.6
AS1109
ND
ND
ND
ND
ND
ND
0.18(a)
0.32
0.33, .
0.45(3)
1.1
1.1
0.57
0.47
0.49
o!58
5.54
AS0918
0.14(a)
ND
ND
ND
ND
0.88
ND
1.7
1.4
1.2
4.4
3.9
2.0
1.1
1.3
0.43
1.6
19.0
AS1113
ND
ND
ND
ND
ND
0.72
ND
2.2
1.9
1.5(3)
3.3
2.0
1.4
1.3
1.0, .
0.22(3)
1.5
16.3
AS1102
ND
ND
ND
ND
ND ,
0.17(3)
ND , .
0.33(3)
0.31
0.22(3)
0.74
1.4
0.64
0.41
0.57
0.12
0.64
5.38
AS1116
ND
ND
ND
ND
ND
ND
ND
0.98(3)
1.0. .
1.5(3)
3.0
3.1, .
2.3(3)
2.4
1.6
ND
2.4
18.3
                                         146
-------
PSWQA  AIR SAMPLING
Particulate PAH Concentrations at Five Tacoma Sites (ng/m3)
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a) anthracene
Crysene
Benzo (b)fluoranthene
Benzo (k)fluoranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Dibenzo (a, h) anthracene
Benzo (g , h , i ) pery 1 ene
TOTAL CPAH
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a) anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k)fluoranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Dibenzo (a ,h) anthracene
Benzo (g , h,i) pery 1 ene
AS1127
ND
ND
ND
ND
ND
5.3
ND
19
1.7.
ll(3)
25
14
9.4
8.6
5.9
1.7
7.2
103
AS1211
ND
ND
ND
ND
ND
4.6(3)
ND
16
17 f ^
19(3)
36
2.3. .
14(3)
17
11
ND
13
AS1130
0.18
ND
ND
ND
ND
1.3. .
0.18(3)
2.8
2.0
5.3
14
9.7
5.1
3.9
2.7
1.0
3.3
49.8
AS1212
ND
ND
ND
ND
ND
3.3
ND
18
16. .
10(3)
22
13
9.8
9.2
5.8
1.8
6.9
AS1204
0.19(a)
ND
ND
ND
ND
0.61
ND
1.3
1.1
1.3(3)
3.2
2.8
1.3
1.4
1.1
0.23'3)
1.4
15.1
AS1213
ND
ND
ND
ND
ND
4.3
ND
15
15
25
14
8.3
8.1
5-2
1.7(3)
8.0
AS1207
0.15(3)
ND
ND
ND
0.12(3)
2.5
0.24
8.1
7.0.
4.6(3)
10
6.7
4.5
3.6
2.5
0.82
3.0
50.8
AS1215
ND
ND
ND
ND
ND
0.60(3)
ND
1.4
1.3
1.0
2.6
1.7
0.30
0.78
0.61
ND
0.91
TOTAL CPAH
145
115
111
10.6
                                         147
-------
PSWQA  AIR SAMPLING
Particulate PAH Concentrations at Five Tacoma Sites (ng/m^)
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a) anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k) f 1 uoranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Di benzo (a , h) anthracene
Benzo (g , h , i ) peryl ene
AS1216
ND
ND
ND
ND
ND
ND
ND , .
2.5 3
1.7(a)
1.6(3)
3.7
2.5(3)
1.4
i ~\
0.89(a)
ND
1.2
AS1218
0.14(3)
ND
ND
ND
ND
1.4
ND
3.5
3.2
3.2(3)
6.1
4.4
3.4
3.5
2.3
0.62
2.8
MS0727
0.13l(3)
ND
ND
ND
ND
0.1572
ND
0.2358
0.2096
0.13l(3)
0.262
0.4978
ND
0.131(3)
0.262
ND
0.4061
MS0814
0.133(3)
ND
ND
ND
ND
0.1729
ND . .
0.266(3)
0.2394
0.133(3)
0.3724
0.7714
ND
0.2527
0.3724
ND
0.665
TOTAL CPAH
 16.7
33.0
2.14
3.07
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k) f 1 uoranthene
Benzo(a)pyrene
Indeno(l,2(3-c,d)pyrene
Di benzo (a , h) anthracene
Benzo (g,h,i) peryl ene
MS0821
ND (3)
ND
ND
ND
ND (^
ND (a)
ND . .
0.28(a)
0.196
ND (3)
0.364
0.42
ND
0.112
ND (3)
ND
0.224
MS1116
0.27(a)
ND
ND
ND
ND
0.47(3)
ND . .
0.88(a)
1.0
1.6
3.1
3.5
2.2
2.7
2.2
0.44(3)
2.6
MS1211
0.39
ND
ND
ND
ND
3.7
ND
15
15
11
21
13
7.4
8.7
5.4
1.3
7.7
MS1215
0.4l(3)
ND
ND
ND
ND
0.38
ND
1.1
1.1, .
1.3(3)
2.8
2.2
1.3
1.3
0.96
0.24
1.4
TOTAL CPAH
1.60
20.2
   106
 13.7
                                         148
-------
PSWQA  AIR SAMPLING
Particulate PAH Concentrations at Five Tacoma Sites (ng/m3)
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo(k)fl uoranthene
Benzo(a) pyrene
Indeno (1 , 2 , 3-c , d) pyrene
Dibenzo(a,h) anthracene
Benzo (g , h , i ) pery 1 ene
RS0727
0.16(3)
ND
ND
ND
ND
0.131
ND
0.295
0.262
0.180
0.787
1.410
ND
0.295
0.443
0.279
0.689
RS0814
o.is(b)
ND
ND
ND
ND
0.193
ND
0.438
0.350
0.193
0.700
0.963
ND
0.263
0.315
0.088
0.543
RS0821
0.291
ND
ND
ND
ND
0.452
ND
0.678
0.484
0.32(3)
0.872
0.872
ND
0.194.
0.32(3)
ND
0.291
RS1116
0.13
ND
ND
ND
ND
0.54
ND
0.12
1.2
2.5(3)
3.6
3.7
3.0
3.5
2.1
0.53
2.4
TOTAL CPAH
4.64
3.85
4.04
22.6
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene '
Pyrene
Benzo(a) anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k) f 1 uoranthene
Benzo (a) pyrene
Indeno(l, 2, 3-c, d) pyrene
Dibenzo (a, h) anthracene
Benzo (g,h,i)perylene
TOTAL CPAH
RS1127
ND
ND
ND
ND
ND
3.1
ND
10
14(3)
19
13
9.4
15
7.4, .
1.5(3)
8.9
109
RS1211
ND
ND
ND
ND
ND
3.2
ND
11
13W
22
15
11
11
7.6
1O I Ct J
• O *
8.2
112
RS1215
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.1
1.1. .
0.72^3)
0.80(3)
0.54(3)
ND
0.80
5.06
SL0727
0.15(a)
ND
ND
ND
ND
0.179
ND
0.373
0.268. .
0.15(3)
0.447
0.894
ND
0.224
0.358
ND
0.417
3.13
                                      149
-------
PSWQA  AIR SAMPLING
Particulate PAH Concentrations at Five Tacoma Sites (ng/m^)
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a)anthracene
Crysene
Benzo (b)fl uoranthene
Benzo (k) f 1 uoranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Dibenzo (a ,h) anthracene
Benzo(g,h,i)perylene
TOTAL CPAH
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a) anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k)fl uoranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Dibenzo (a ,h) anthracene
Benzo(g,h,i)perylene
SLOSH
o.isO>)
ND
ND
ND
ND
0.247
ND
0.392
0.305
0.160
0.493
0.464
0.348
0.29'a)
0.334
0.15(a)
0.551
3.48
TM0727
0.091
ND
ND
ND
ND
0.160
ND
0.319
0.274
0.23'a)
0.661
0.821
ND
0.228
0.182. .
ND (a)
0.274
SL0821
ND
ND
ND
ND
ND
0.380
ND
0.654
0.549
0.42'a)
0.760
0.823
0.675
0.485
0.654
ND
0.717
5.74
TM0814
0.280>)
ND
ND
ND
ND
0.165
ND
0.28(a)
0.138. .
ND (a)
0.247
0.55'a)
ND
0.28jaj
0.28'a)
ND
0.385
SL1116
0.16(a)
ND
ND
ND
ND
0.31
ND
0.81
0.94
1.6'a'
3.1
3.4
1.9
2.3
1.7
0.48
2.2
18.4
TM0821
ND
ND
ND
ND
ND
0.258
ND
0.386
0.322
ND
0.451
0.483
ND
ND
ND
ND
0.258
SL1211
ND
ND
ND
ND
ND
5.0.
0.42(a)
18
17(^
12(a)
23
14
10
10
6.4
1 .4(3)
8.1
120
TM0828
0.26
ND
ND
ND
ND
0.16
ND
0.29
0.22. .
0.066(a)
0.20
0.19.
0.068(a)
0.10
0.1
ND
0.19
TOTAL CPAH
2.99
2.15
1.90
1.42
                                         150
-------
PSWQA  AIR SAMPLING
Particulate PAH Concentrations at Five Tacoma Sites (ng/m^)
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anthracene
Crysene
Benzo(b)fl uoranthene
Benzo(k) f 1 uoranthene
Benzo(a)pyrene
Indeno ( 1 , 2 , 3-c , d) pyrene
Dibenzo (a, h) anthracene
Benzo (g , h , i ) pery 1 ene
TM0911
0.12(3)
ND
ND
ND
ND
0.46
ND
1.1
0.85
0.66
2.4
5.0
ND
0.66
0.77
0.33
0.91
TM1116
0.12(3)
ND
ND
ND
ND
0.37
ND
1.1
1.2
2.8
7.0
5.0
2.9
2.5
1.5
0.59
1.6
' TM1211
0.55(3)
ND
ND
ND
ND
5.5.
0.74'3)
*34
33
30
68
33. .
14(3)
12
7.0
3.2
7.8
TM1215
ND
ND
ND
ND
ND
ND
ND . .
2.9 a
2.6 a
2.2(3)
6.3
3.8
ND
ND
ND
ND
l.l(3)
TOTAL CPAH
12.7
 26.2
  242
 18.9
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a) anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo ( k) f 1 uoranthene
Benzo(a) pyrene
Indeno(l,2,3-c,d)pyrene
Dibenzo (a ,h) anthracene
Benzo (g,h,i)peryl ene
TM1216
ND
ND
ND
ND
ND
ND
ND . .
1.7 a
X • / / »
1.9(3)
2.3
6.5
3.9
2.2. .
1.7(3)
1.0
ND
1.4
DTM0727
0.2l(3)
ND
ND
ND
ND
0.385
ND
0.556
0.428
0.257
0.877
0.877
ND
0.2l(3)
0.193
ND
0.257
DTM0814
ND (b)
ND
ND
ND
ND
0.0885
ND
0.0885
0.059
ND
0.1475
0.3245
ND
ND (3)
0.1475
ND
0.2655
DTM0821
ND (3)
ND
ND
ND
ND , ,
ND (3)
ND
0.343
0.2401
ND U)
0.4459
0.5145
ND
0.1372. .
ND (3)
ND
0.2744
TOTAL CPAH
 22.6
3.66
1.03
1.96
                                         151
-------
PSWQA  AIR SAMPLING


Participate PAH Concentrations at Five Tacoma Sites (ng/nr)


Compound                   BP0828        BP0911        BP1109
Naphthalene                  ND            0.28          ND
Acenaphthalene               ND            ND            ND
Acenaphthene                 ND            ND            ND
Fluorene                     ND            ND            ND
Dibenzothiophene             ND            ND            ND
Phenanthrene                 ND            0.33          ND
Anthracene                   ND            ND            ND
Fluoranthene                 ND            0.98          O.
Pyrene                       ND            0.82          0.03}aj
Benzo(a)anthracene           ND            0.67          0.04V3)
Crysene                      ND             2.4          0.12
Benzo(b)fluoranthene        0.090           5.2          0.14
Benzo(k)fluoranthene         ND            ND           0.071
Benzo(a)pyrene               ND            0.63         0.054
Indeno(l,2,3-c,d)pyrene     0.070          0.74         0.063.
Dibenzo(a,h)anthracene       ND            0.30         0.01l(a)
Benzo(g,h,i)perylene         0.16          0.96         0.069

TOTAL CPAH                   0.32          12.7         0.628
(a)  Ion Ratios Out

(b)  Analyte in Blank
                                        152
-------
Appendix C-6.  Vapor PAH Concentrations
                                      153
-------
PSWQA Air  Sampling
Vapor PAH  Concentrations  (ng/m^)
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anth racene
Crysene
Benzo (b)f 1 uoranthene
Benzo (k) f 1 uoranthene
Benzo (a) py rene
Indeno (1,2, 3-c , d) py rene
D i benzo (a , h) anth racene
Benzo (g,h, i)pery lene
AS0724
0.084
0.029
0.29
1.5
3.0
38
3.3
20
11
0.47
1.4
0.16
ND
ND
ND
ND
ND
TM0727
0.150
0.150
0.458
2.22
4.51
34
0.608
8.4
4.8
0.057
0.251
0.050
ND
ND
ND
ND
ND
DTM0727
0.139
0.163
0.581
3.02
4.96
29
1.08
7.3
4.2
0.064
0.302
0.042
0.008
ND
ND
ND
ND
MS0727
0.415
0.176
0.514
1.62
1.48
15
0.633
7.2
4.08
0.070
0.246. ,
0.02^
ND
ND
ND
ND
ND
SL0727
0.184
0.048
0.585
1.59
1.84
28
1.00
14
7.4
0.125
0.577 . .
0.03^
0.0llaJ
ND
ND
ND
ND
AS0727
0.434
0.171
1.71
3.72
2.02
36
1.63
15
7.9
0.178
0.729
0.093
ND
ND
ND
ND
ND
RS0727
0.320
0.125
0.195
1.64
1.17
18
0.389
7.24
3.74
0.156
1.01
0.187
ND
ND
ND
ND
ND
AS0803
2.76
0.115
23
60
4.15
600
120
120
61
0.561
1.08 , .
0.04(a)
0.01^
ND
ND
ND
ND
TOTAL PAH
79.2
55.7
43.5
31.5
55.4
69.6
34
992.7
COB pound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anth racene
Crysene
Benzo (b) f 1 uo ranthene
Benzo (k) f 1 uoranthene
Benzo (a) py rene
Indeno (1 , 2 , 3-c , d) py rene
Dibenzo(a,h) anth racene
Benzo (g,n(i)pery lene
TM0814
0.260
0.048
0.260
2.20
1.20
21.0
1.10
6.40
3.80
0.140
0.490
0.100
ND
ND
ND
ND
ND
DTM0814
0.235, .
0.05
0.255
2.16
1.08
20
0.97
5.9
3.4
0.157
0.412
0.056
0.015
ND
ND
ND
ND
MS0814
0.161
0.047
0.160
1.23
1.71
28
0.7S9
2.85
2.09
0.051
0.152. .
0.02^
ND
ND
ND
ND
ND
SL0814
0.489
0.085
0.675
3.33
3.62
34
2.05
10
5.87
0.089
0.362 , .
0.01^
ND
ND
ND
ND
ND
AS0814
0.236 . .
0.04^
0.907
3.49
3.31
66
3.12
24
13
0.123
0.406
0.018
ND
ND
ND
ND
ND
RS0814
0.666
0.472
1.54
4.51
1.44
21
1.03
6.77
4.10
0.113
0.615
0.072
ND
ND
ND
ND
ND
TOTAL PAH
37.0
 150
37.2
                                                60.6
                                  134.6
                   42
                                            155
-------
PSWQA Air Sampling
Vapor PAH Concentrations
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k) f 1 uoranthene
Benzo(a)pyrene
Indeno (1 , 2 , 3-c , d) py rene
Dibenzo (a ,h) anthracene
Benzo (g,h, i)perylene
TM0821
0.491
0.378
1.00
3.17
1.43
18
0.685
3.99
2.25
0.00
0.083
0.00
ND
ND
ND
ND
ND
DTM0821
0.391
0.341
0.963
3.61
1.91
18
0.863
4.3
3.91
0.042
0.241
0.038
ND
0.019
ND
ND
ND
MS0821
0.746
0.962
1.08
3.34
1.47
22
1.28
6.38
4.52
0.076
0.275
0.008
ND
ND
ND
ND
ND
SL0821
0.514
0.534
0.826
3.22
3.93
30
1.71
8.6
5.2
0.101
0.483
0.022
ND
ND
ND
ND
ND
AS0821
3.57
0.419
1.47
5.45
4.93
56
3.88
15
9.3
0.587
1.36
0.083
ND
ND
ND
ND
ND
RS0821
0.954
0.518
0.819
1.45
1.24
18
0.736
4.25
2.38
0.057
0.311
0.052
ND
ND
ND
ND
ND
AS0911
0.411
0.802
2.706
9.019
7.817
100
6.113
55.119
29.063
1.102
5.712
ND
ND
ND
ND
ND
ND
TOTAL PAH
31.5
38.2
                                         42.1
55.1
102.0
31
                                                      217.9
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a)anthracene
Crysene
Benzo (b)f 1 uoranthene
Benzo (k)f luoranthene
Benzo (a) py rene
Indeno (1 , 2, 3-c , d) py rene
Dibenzo (a, h) anthracene
Benzo (g,h, i)perylene
AS0828
1.14
0.836
1.67
4.86
3.49
50.9
3.11
19.7
10.6
0.289
1.14
0.084
ND
ND
ND
ND
ND
BP0828
0.745
0.00
0.00
0.670
0.335
4.39
0.00
1.86
1.34
0.00
0.149
0.00
ND
ND
ND
ND
ND
AS0907
1.66
0.948
2.29
7.90
7.74
130
10.3
60.0
32.4
0.766
4.03
ND
ND
ND
ND
ND
ND
TM0911
1.2
0.60
3.0
7.2
4.3
54
1.8
24
13
1.4
7.1
0.57
ND
ND
ND
ND
ND
BP0911
0.99
0.76
2.4
5.2
1.8
63
2.7
33
21
1.8
8.6
0.21^a'
ND
ND
ND
ND
ND
AS0914
0.182
0.00
0.407
2.74
4.07
53
4.00
28.8
16.4
0.568
2.67
1 ND
ND
ND
ND
ND
ND
AS0918
0.238
0.00
0.742
3.20
9.16
150
8.79
49.4
29.3
1.37
5.40
0.00
ND
ND
ND
ND
ND
TOTAL PAH
97.9
                               9.50
                                        258.1
                                                 118.3
                                   140.76
                                                                   111.8
                                                                            257.7
                                             156
-------
PSWQA Air Sampling
Vapor PAH Concentrations  (ng/n)3)
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a)anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k)f 1 uoranthene
Benzo(a)pyrene
Indeno (1,2, 3-c , d) py rene
Dibenzo(a,h) anthracene
Benzo (g , h , i ) pery 1 ene
AS1102
0.311
0.297
1.04
2.82
3.26
49.7
2.16
17.8
11.9
0.652
2.00
ND
ND
ND
ND
ND
ND
AS1113
1.29
2.67
1.78
9.69
11.9
99
8.61
28.7
20.8
0.712
1.48
ND
ND
ND
ND
ND
ND
MS1116
0.688
1.74
0.611
6.28
8.30
66
7.32
18.9
16.8
0.619
1.13
ND
ND
ND
ND
ND
ND
SL1116
0.606
1.68
0.641
6.69
10.3
71
7.28
20.6
16.8
0.767
1.60
ND
ND
ND
ND
ND
ND
AS1127
7.74
11.6
8.20
38.7
23.4
200
18.8
67.4
37.6
0.646
0.938
0.00
ND
ND
ND
ND
ND
AS1130
0.22
0.29
1.02
2.71
21.2
300
19.6
89
61
4.24
9.33
0.117
ND
ND
ND
ND
ND
AS1204
9.95
3.27
27.5
23.6
15.7
150
10.5
39.3
27.5
1.26
2.76
ND
ND
ND
ND
ND
ND
TOTAL PAH
 91.9
186.5
125.3
135.6
404.7
                                             508.6
311.2
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Di benzoth i ophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anth racene
Crysene
Benzo (b)f 1 uoranthene
Benzo (k)f 1 uoranthene
Benzo (a) py rene
Indeno (1 , 2 , 3-c , d) py rene
Di benzo (a , h) anthracene
Benzo (g, h, ijpery lene
TM1211
0.81
7.2
20
45
30
360
35
100
75
0.63
1.1
ND
ND
ND
ND
ND
ND
MS1211
5.4
13
8.7
40
23
120
14
28
24
0.16
0.27
ND
ND
ND
ND
ND
ND
SL1211
3.3
8.8
13
44
21
121
13
25
20
0.maJ
0.35
ND
ND
ND
ND
ND
ND
AS1211
9.5
10
5.6
26
20
130
27
57
39
1 0.37
0.62
ND
ND
ND
ND
ND
ND
RS1211
7.2
17
1.6
12
8.5
67
10
21
17
0.32
0.56
ND
ND
ND
ND
ND
ND
AS1218
2.41
4.48
5.25
18.6
12.0
100
9.62
30.6
20.8
0.547
1.03
ND
ND
ND
ND
ND
ND
AS1106
0.71
0.74
2.9
6.0
6.4
6.0
2.8
12
7.4
ND
0.81
ND
ND
ND
ND
ND
ND
TOTAL PAH
674.7
                               276.5
                  269.6
                  325.1
                    162
                  205.3
                   45.5
                                              157
-------
PSWQA Air  Sampling
Vapor PAH  Concentrations  (ng/m^)
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anthracene
Crysene
Benzo (b)f 1 uoranthene
Benzo(k)f 1 uoranthene
Benzo (a) py rene
Indeno (1 , 2 , 3-c , d) py rene
Dibenzo (a ,h) anthracene
Benzo (g,h, ijpery lene
MS1214
• .12«
1.8
0.70
5.5
11
72
9.9
25
20
0.57
0.99
ND
ND
ND
ND
ND
ND
AS1214
1.5
2.0
0.89
5.9
8.1
89
8.9
38
26
0.50
0.81
ND
ND
ND
ND
ND
ND
TM1214
0.74
1.1
0.48
5.7
15
173
16
55
41
0.95
2.2
ND
ND
ND
ND
ND
ND
RS1214
0.95
1.8
0.30
3.0
2.5
36
4.8
11
10
0.30
0.42
ND
ND
ND
ND
ND
ND
AS 1207
7.14
8.81
4.40
15.0
12.3
120
12.3
44.9
31.7
1.59
4.40
ND
ND
ND
ND
ND
ND
TOTAL PAH
                              147.6
181.6
311.2
                   71
                         262.6
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anthracene
Crysene
Benzo (b)f 1 uoranthene
Benzo(k)f 1 uoranthene
Benzo (a) py rene
Indeno (l,2,3-c,d)py rene
Dibenzo (a, h) anthracene
Benzo (g,h, i)pery lene
TOTAL PAH
TM0828
0.657
ND
0.332
1.74
1.06
10.6
0.355
3.70
2.11
ND
0.106
ND
ND
ND
ND
ND
ND
20.6
RS1127
6.61
14.9
6.82
22.7
8.26
116
16.5
26.9
20.7
0.661
0.888
ND
ND
ND
ND
ND
ND
241
AS1116
0.33
1.5
0.79
11
14
140
14
51
35
1.7
4.1
ND
ND
ND
ND
ND
ND
273.1
TM1116
0.000
0.547
0.46
6.57
9.38
140
0.98
31.3
23.5
1.17
2.66
ND
ND
ND
ND
ND
ND
216.5
BP1109
0.17^
ND
ND
0.67
0.98
13
0.61
4.3
3.0
0.11
0.48
ND
ND
ND
ND
ND
ND
23.32
AS1109
i.26<«
0.40
0.82
3.1
4.7
48
2.8
14.5
9.5
0.23
0.76
ND
ND
ND
ND
ND
ND
85.0
RS1118
') 0.296
1.559
0.351
4.053
3.507
87.027
7.794
21.823
16.367
1.013
1.793
ND
ND
ND
ND
ND
ND
126
(a)  Ion Ratios Out
                                           158
-------
Appendix C-7. Particulate and Vapor Aliphatics and PCBs
                                      159
-------
Compound

  n-C09
  n-CIO
  n-Cll
  P-C12
  n-C13
  n-C14
  n-C15
  n-C16
  P-C17
PRISTANE
  n-C18
PHYTANE
  n-C19
  P-C20
  n-C21
  n-C22
  n-C23
  P-C24
  n-C25
  n-C26
  P-C27
  n-C28
  n-C29
  n-C30
  n-C32
  n-C34
  n-C36

TOTAL

% Surrogate
  recovery
10.99
 94
                                    Concentrations  of  Particulate  Aliphatic  Hydrocarbon
                                    Compounds Collected  in Air  Samples from Tacoma
                                    (July  to December 1989)

                                                                 Sample No.  pg/m
SL0727
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.66
2.01
3.37
1.67
1.28
ND
ND
DTH0727
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.42
0.93
ND
ND
ND
/^S0727
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
4.92
6.74
7.29
7.53
5.27
6.16
3.01
1.72
ND
ND
HS0727
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.74
2.48
1.85
2.46
3.11
2.06
ND
2.96
1.92
ND
ND
ND
MS1211
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
6.72
3.81
13.32
34.30
60.74
ND
ND
ND
ND
ND
ND
ND
ND
ND
8.68
6.87
ND
SL1211
ND
ND
ND
ND
ND
ND
ND
ND.
ND
ND
5.01
ND
9.20
23.38
48.61
50.76
ND
ND
ND
ND
ND
ND
ND
14.38
6.62
7.09
ND
TH1211
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
4.67
13.49
33.81
42.86
56.16
ND
33.28
24.31
19.13
17.18
12.92
7.01
6.90
ND
ND
AS1211
2.43
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.23
3.45
7.95
9.07
8.80
5.93
4.63
3.17
4.39
2.43
2.89
2.13
1.47
ND
ND
RS1211
ND
NO
ND
ND
ND
ND
ND
ND
NO
ND
NO
ND
ND
NO
ND
20.05
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
ND
3.35
90
42.64
94
18.58
93
134.44
 82
165.05
 87
271.72
 81
                                                                                     59.97
                                                                                     89
                                                                                    20.05
                                                                                    91
-------
ts>
 n-C09
 n-CIO
 n-Cll
 n-C12
 n-C13
 n-C14
 n-C15
 n-C16
 n-C17
 Pristane
 n-C18
 Phytane
 n-C19
 n-C20
 n-C21
 n-C22
 n-C23
 n-C24
 n-C25
 n-C26
 n-C27
 n-C28
 n-C29
 n-C30
 n-C32
 n-C34
 n-C36

TOTAL

% Surrogate
  Recovery
                                29.05
                                72
                                                Concentrations of  Vapor Aliphatic Hydrocarbon  Compounds
                                                 Collected  in Air Samples  from Tacoma  (July  to December 1989)
                                                                                            3
                                                                               Sample No. ng/m
SL0727
ND
NO
ND
ND
ND
ND
0.22
0.94
ND
ND
ND
ND
ND
4.88
ND
20.62
ND
ND
ND
ND
ND
0.44
0.59
0.51
0.49
0.36
ND
DTM0727
ND
ND
ND
ND
ND
7.40
11.54
18.45
14.87
ND
57.86
ND
ND
14.96
ND
ND
ND
ND
ND
5.90
ND
ND
ND
ND
2.83
ND
ND
AS0727
ND
ND
ND
ND
ND
0.70
0.63
1.35
3.77
1.95
4.61
2.52
7.15
ND
ND
ND
ND
ND
ND
1.85
0.55
0.49
0.58
0.50
0.54
ND
ND
HS0727
ND
ND
ND
ND
0.24
ND
0.46
0.65
2.19
2.08
3.92
ND
ND
3.68
ND
ND
ND
ND
ND
ND
0.33
ND
0.57
0.51
0.51
0.38
ND
MS1211
ND
ND
ND
ND
ND
11.53
17.74
30.69
ND
26.47
ND
ND
ND
ND
ND
12.30
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
SL1211
ND
ND
ND
ND
ND
15.24
23.93
45.27
118.86
37.43
ND
145.90
206.25
ND
ND
12.87
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TM1211
ND
ND
ND
ND
ND
5.85
8.68
27.53
ND
ND
80.44
82.58
103.11
ND
30.81
9.73
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
AS1211
ND
ND
ND
1.16
1.96
3.96
12.88
10.54
ND
ND
30.12
ND
35.84
ND
ND
4.82
ND
ND
ND
ND
ND
ND
ND
2.02
ND
ND
ND
RS1211
ND
ND
ND
ND
ND
6.24
ND
ND
15.98
ND
20.88
20.37
28.32
20.80
11.77
7.28
ND
ND
ND
ND
ND
ND
ND
5.61
ND
ND
ND
133.81
409
27.3
58
15.01
70
 98.73
153
605.75
171
348.73
137
103.3
                                                                                                                     134
116.93
            87
-------
                                         Concentrations  of Particulate PCB Congeners
                                          in Air Samples from Tacoma (July to December  1989)
                                                                            3
                                                                Sample No. ng/m
Congener No.

   18
   33
   52
   49
  101
   97
   77
  149
  118
  114
  153/105
  137
  138
  126
  187
  157
  180
  169
  195
  194

TOTAL

% Surrogate
  recovery
SL0727
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
DTM0727
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.01
ND'
ND
ND
ND
ND
ND
ND
AS0727
ND
ND
ND
ND
ND
ND
ND
ND
0.04
ND
ND
ND
0.005
ND
ND
ND
ND
ND
ND
ND
HS0727
0.006
ND
ND
0.018
ND
ND
ND
ND
ND
ND
0.001
ND
0.009
ND
ND
ND
0.006
0.003
ND
0.00
MS1211
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
SL1211
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TH1211
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.37
ND
ND
ND
ND
ND
ND
ND
AS1211
ND
NO
0.08
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.07
ND
ND
ND
ND
ND
ND
ND
RS1211
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
79
 0.01
80
 0.045
81
 0.043
81
ND
66
ND
73
 0.37
60
 0.15
76
ND
63
-------
                                                    Concentrations of Vapor  PCB  Congeners
                                                    Collected  in Air  Samples from  Tacoma
                                                    (July  to December 1989)
Congener No.

   18
   33
   52
   49
  101
   97
   77
  149
  118
  114
  153/105
  137
  138
  126
  187
  157
  180
  169
  195
  194

TOTAL                0.17        0.07        0.008        0.04         1.32         1.65        1.31         0.35        0.38

%  Surrogate
  recovery           88          85          58          85         104           93          92          93         89
Sample No. rig/m
SL0727
ND
0.17
ND
NO
ND
NO
ND
ND
ND
ND
NO
ND
ND
ND
ND
ND
ND
ND
ND
ND
DTM0727
ND
ND
ND
ND
0.04
ND
ND
ND
0.03
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
AS0727
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.007
ND
ND
ND
ND
0.001
ND
MS0727
ND
ND
ND
ND
ND
ND
ND
ND
0.04
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
MS1211
ND
1.11
ND
ND
ND
ND
ND
ND
0.21
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
SL1211
ND
1.07
0.44
ND
ND
ND
ND
ND
0.14
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TM1211
ND
0.94
ND
ND
ND
ND
ND
ND
0.24
ND
0.13
ND
ND
ND
ND
ND
ND
ND
ND
ND
AST 211
ND
0.30
ND
ND
ND
ND
ND
ND
0.05
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
RS1211
ND
ND
0.31
ND
ND
ND
ND
ND
0.07
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
Appendix C-8.  Deposition Metals
                                        165
-------
Concentrations of Metals in Atmospheric Deposition
Samples Collected in Tacoma During July to December, 1989
Site

Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea 1 and
Alexander Street
Riverside School

Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School
volume
(L)


1.59
2.23
1.80
1.65
1.
2

,98
,14

1.72
2.02
1.39
2.26
1.86
3.09


2.20
3
.80
4.35
2.45
1
4
.50
.02
As
July 13,
1.41
1.30
9.60
8.28
17.57
1.50
July 27,
1.92
1.58
15.03
15.93
22.40
1.53
August 10
0.73
1.21
9.41
20.42
22.66
1.02
Cr
1989-
2.82
2.82
15.7
38.4
13.4
3.78
1989 —
5.51
5.24
26.8
21.5
27.3
2.96
, 1989
6.91
2.02
0.40
28.0
19.4
3.36
August 24, 1989
Tyee Marina
Morse Supply
Sea 1 and
Alexander Street
Riverside School
0
0
0
1
1
.79
.33
.72
.04
.94
1.69
21.81
36.33
5.08
1.13
4.91
6.83
23.2
11.4
2.91
Cu
July 27, 1989
16.37
19.72
157.4
183.3
83.76
13.39
Mn

34.7
26.5
218
66.8
119
37.5
Ni

7.42
6.49
53.6
58.7
23.9
9.04
Pb

33
30
141
620
60
17


.9
.3
.7
.6
.6
.3
Zn

74
83
313
1234
207
42
August 10, 1989
32.37
37.76
213.18
137.47
93.64
26.97
— August 24,
22.88
11.91
135.48
179.31
87.66
16.25
— September 7
41.22
440.31
322.76
77.7
15.28
57
37.5
272
156
196
40.3
1989
44.5
22.3
140.3
224
161
26.5
, 1989
55.6
552
267
103
34.4
8.36
8.1
60.9
44.8
43.6
9.04

8.6
4.6
39.2
47.8
38.7
4.17

16.1
194.1
76.4
29.5
9.68
50
30
187
296
95
17

35
29
112
606
87
11

80
362
1546
70
24
.9
.3
.8
.0
.7
.0

.1
.1
.7
.0
.2
.3

.3
.8
.7
.7
.6
199
127
723
1780
378
35

156
82
248
1093
340
22

186
934
1861
271
42
September 7, 1989 — September 21, 1989
Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Morse Supply
Sea 1 and
Alexander Street
Riverside School
0
1
1
1
0
2

11
7
8
11
14
.89
.48
.12
.04
.50
.17

.35
.67
.24
.69
.17
3.47
0.93
26.67
85.65
47.34
1.84
November
0.55
0.98
1.41
1.07
0.12
7.21
4.14
3.63
6.75
6.59
9.51
73.72
33.41
143.46
616.03
364.6
19.72
85.6
45.6
627
514
629
44.4
20.9
12.2
108.2
85.9
194.1
14.6
62
32
276
4677
305
27
.1
.1
.9
.7
.5
.9
165
85
511
1974
1216
53
2, 1989 - November 16, 1989
1.16
3.49
1.83
2.16
0.66
2.79
24.98
10.45
6.62
< 0.52
8.96
28.2
12.1
10.6
2.21 <
4.97
9.23
2.60
1.89
0.71
7.
27
36
5.
2.
21
.0
.3
93
67
18
45
40
40
3.2
                                     167
-------
Concentrations of Metals in Atmospheric Deposition
Samples Collected in Tacoma During July to December,
1989
Site

Tyee Marina
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Morse Supply
Sea land
Alexander Street
Alexander Street (dup)
Riverside School

Tyee Marina
Morse Supply
Sea land
Alexander Street
Riverside School
volume
(L)

4.33
7.44
6.64
4.64
7.45

9.25
7.02
11.30
11.40
9.73
12.65

1.62
1.60
1.24
2.28
1.94
As
November
0.77
0.83
2.09
1.41
0.34
November
0.29
1.15
1.79
0.80
0.82
0.26
December
2.26
6.55
15.03
2.26
0.65
Cr
16, 1989
1.50
2.33
1.99
2.16
0.83
30, 1989
1.16
2.49
1.99
1.50
1.33
1.18
14, 1989
6.37
10.7
11.7
4.75
1.38
Cu
— November
21.42
6.62
10.28
16.03
4.53
— December
20.73
11.85
19.63
10.45
7.49
0.87
— December
227.13
63.76
77.7
43.71
16.52
Mn
30, 1989
13.3
42.3
17.0
25.9
8.44
14, 1989
7.40
12.2
12.0
9.48
8.05
4.29
28, 1989
45.6
58.9
68.9
44.4
15.6
Ni

10.2
11.1
6.87
11.1
0.95

5.92
6.87
6.63
7.58
6.63
1.42

35.4
33.1
42.1
28.4
4.73
Pb

9.65
19.7
36.3
8.37
3.72

4.42
10.7
28.0
3.61
3.95
1.51

25.7
46.1
96.4
17.1
10.7
Zn

34
26
45
48
9.6

21
30
32
26
14
6.4

72
101
181
61
16
                                     168
-------
Deposition  Rate of Metals  in Tacoma Deposition Samplers
Collected  During July  to  December, 1989
                               Deposition Rate (jug/i2/day)
Site
As Cr
Cu
Mn
Ni
Pb
Zn
July 13, 1989 - July 27, 1989
Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School
1.32 2.28
1.71 3.28
10.27 16.38
8.12 37.30
20.69 15.30
1.90 4.27
14.41
24.65
167.35
178.84
73.77
15.60
32.34
34.47
232.92
65.07
139.58
47.09
6.02
7.20
56.27
56.59
26.91
10.16
31.63
39.58
151.26
608.81
70.84
21.43
65.97
104.46
330.65
1207.29
238.84
48.04
July 27, 1989 - August 10, 1989
Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Morse Supply
Sea 1 and
Alexander Street
Riverside School
1.95 5.22
1.89 5.81
12.42 21.83
21.41 28.36
24.78 29.76
2.79 4.69
August 10, 1989 -
0.94 7.20
2.71 3.64
24.33 < 0.34
29.75 40.22
20.22 16.95
2.42 7.06
August 24, 1989 -
0.79 2.12
4.28 1.06
15.56 9.75
3.14 6.80
1.29 2.89
September 7, 1989
1.83 3.60
0.81 3.28
17.77 2.08
52.99 3.92
14.08 1.84
2.36 11.75
November 2, 1989
3.65 5.06
4.43 14.06
6.86 6.96
7.37 12.17
0.93 2.11
31.96
44.01
176.37
183.32
102.37
47.49
August 24
28.46
24.35
347.71
259.73
77.22
33.75
September
18.84
86.23
137.78
47.38
16.32
57.80
44.45
224.53
209.07
216.34
73.14
, 1989
57.57
49.24
361.79
325.78
143.23
62.14
7, 1989
25.89
108.28
114.16
63.41
39.11
7.46
8.46
41.22
58.82
47.08
14.67

9.87
8.00
98.72
68.14
33.69
7.44

6.60
37.90
32.28
17.60
9.95
51.61
35.85
154.93
397.40
105.39
30.39

45.33
64.73
290.46
736.94
77.41
25.90

37.52
71.14
662.40
43.46
27.85
199.29
147.51
594.43
2387.82
413.61
56.50

197.31
175.75
630.83
1587.10
299.64
42.41

85.42
182.55
795.42
165.05
43.55
- September 21, 1989
38.43
28.42
94.84
318.61
108.13
23.99
- November
11.14
108.80
45.65
38.12
<4.38
45.05
39.70
350.85
317.74
186.97
56.66
16, 1989
57.00
126.32
56.77
70.11
14.25
10.61
9.81
71.40
52.50
57.43
17.48

26.41
37.29
7.55
5.77
<5.99
32.64
27.85
184.21
2894.27
90.75
35.42

45.52
121.07
175.87
37.98
18.55
85.11
71.09
337.68
1218.87
360.49
62.92

92.72
185.88
175.18
248.52
<13.49
                                        169
-------
Deposition  Rate of Metals  in Tacoma  Deposition Samplers
Collected During  July to December,  1989
  Site
Tyee Marina
Morse Supply
Sea I and
Alexander Street
Riverside School
        As
Cr
                        Cu
Mn
Ni
                      November 16, 1989   November 30, 1989
                   Pb
                                              Zn
1.96
3.63
8.22
3.87
1.46
2.81
8.50
6.24
4.83
1.86
52.25
24.26
36.11
41.11
15.03
32.93
184.95
65.11
70.07
35.11
23.55
44.45
22.95
27.72
<3.15
23.65
85.13
141.56
21.81
14.41
76.59
96.19
160.92
120.73
23.83
                      November 30,  1989   December 14, 1989
Tyee Marina
Morse Supply
Sea I and
Alexander Street
Alexander Street
Riverside School
Tyee Marina
Morse Supply
Sea I and
Alexander Street
Riverside School
(dup)
1.54
4.76
11.
5.
97
,36
4.13 107.
8.69 44.
10.62 124,
7
4.75
1.
.88
December
5
14
.39
7.70
.65
, 1989
63.

<3
.82
,73
.32
.15
43.38
.91
December
37.87 26.
48.79 24.
77
60

28
28
.19 37.
.78 44,
46.62
.38 2.
, 1989
.75
27
21.74 92.08
42.73 107.47

.45 185.10 186.44
23
38.40
,71

21.30 147.39
22.88 81
7.83 16.03


.08


2.17
6.23
11.08
3.05
0.74
4.78
9.83
8.30
5.89
1.12
217.83
59.61
56.49
57.75
17.75
43.45
55.58
50.45
59.53
17.41
33.10
30.50
30.28
37.09
4.24
Mean Blank              0.01     0.41      1.14      0.52

Note:   Mean blanks have been subtracted from sample values.
                                          1.06
                                                   24.32
                                                   43.44
                                                   70.78
                                                   22.56
                                                   11.81
                                    0.47
                                             65.28
                                             92.09
                                            130.39
                                             76.96
                                             13.54
                             4.27
                                                  170
-------
Appendix C-9. Nutrient Data
                                       171
-------
Deposition Rate  of Nutrients  in  Tacoma  Deposition  Samplers
Collected  During July to December,  1989
Site
          Nitrate
             ft    Ainonia      Total
Chloride   Nitrite  Nitrogen   Phosphate
 Ortho-
phosphite  Sulfate

Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School
July 13, 1
1.51
2.26
1.39
2.55
3.18
1.02
989 - July
0.33
0.45
0.08
0.04
0.53
0.43
27, 1989
0.61
0.55
0.41
0.36
0.47
1.03

0.06
0.07
0.18
0.09
0.10
0.05

< 0.00
0.03
0.02
0.01
< 0.00
0.02

7.57
9.55
10.92
22.68
18.61
10.44
 Tyee Marina
.Tyee Marina (dup)
 Morse Supply
 Sea I and
 Alexander Street
 Riverside School
 Tyee Marina
 Tyee Marina (dup)
 Morse Supply
 Sea I and
 Alexander Street
 Riverside School
 Tyee Marina
 Alexander Street (dup)
 Morse Supply
 Sea I and
 Alexander Street
 Riverside School
 Tyee Marina
 Alexander Street  (dup)
 Morse Supply
 Sea I and
 Alexander Street
 Riverside School
 Tyee Marina
 Alexander Street  (dup)
 Morse Supply
 Sea I and
 Alexander Street
 Riverside School
                       August 10,  1989 - August 24, 1989
3.40
3.84
<1.29
2.62
3.66
<1.20
September
2.44
3.17
2.87
2.54
2.05
<0.65
October 5
10.99
2.62
<1.13
2.37
2.84
2.20
Novel be r
24.99
5.04
3.97
3.63
5.56
< 4.22
November
9.91
2.95
< 2.09
< 2.35
< 2.31
< 3.76
0.22
0.65
0.07
< 0.01
0.14
0.32
7, 1989
0.50
0.98
0.67
0.20
0.30
0.62
, 1989 -
0.79
1.00
0.88
0.75
0.87
0.78
2, 1989 •
0.16
0.33
0.21
0.24
1.18
0.47
30, 1989
0.37
0.38
0.44
0.56
1.17
0.32
0.68
0.17
0.16
0.03
0.68
0.38
- September
0.50
1.51
0.14
0.60
2.39
0.50
October 19,
0.44
0.32
0.15
0.30
0.24
0.86
0.15
0.03
0.41
0.10
0.21
0.13
21, 1989
0.05
0.15
0.46
0.14
0.29
0.18
1989
0.09
0.12
0.34
0.17
0.11
0.08
• Noveiber 16, 1989
0.16
0.33
0.21
0.24
0.22
0.47
- Deceiber
0.37
0.21
0.44
0.26
0.24
0.32
0.12
0.12
0.46
0.32
0.22
0.07
14, 1989
0.08
< 0.01
0.34
0.17
0.16
0.05
0.06
0.26
< 0.01
< 0.00
0.03
< 0.00
< 0.00
< 0.00
0.20
< 0.00
0.00
< 0.00
< 0.00
< 0.00
< 0.00
< 0.00
< 0.00
< 0.00
< 0.01
< 0.01
0.07
'< 0.00
< 0.01
< 0.01
< 0.01
< 0.01
0.03
< 0.01
< 0.01
< 0.01
5.63
12.89
5.69
30.32
21.69
6.22
12.50
12.59
50.58
46.35
35.70
4.91
290.99
32.25
49.42
24.64
33.41
19.98
35.12
20.94
16.89
12.75
22.26
7.59
20.36
18.53
10.44
16.14
22.38
11.29
 Note:  Blanks  not subtracted froi sanple values.
                                                  173
-------
Concentrations of Nutrients in Atmospheric
Deposition Samples Collected  in Tacoma
During July to December, 1989
                                   (•fl/LJ
Site

Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Tyee Marina (dup)
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Alexander Street
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Alexander Street
Morse Supply
Sea land
Alexander Street
Riverside School

Tyee Marina
Alexander Street
Morse Supply
Sea land
Alexander Street
Riverside School
Volune
(L)

1.
2.
1.
1.
1.
2.

2.
3.
4.
2.
1.
4.

0.
1.
1.
1.
0.
2.


59
23
80
65
98
14

20
80
35
45
50
02

89
48
12
04
50
17

1.71
(dup) 1.78
3
.81
1.02
1.91
3

11
(dup) 11
7
8
11
14

9
(dup) 9
7
11
11
12
.08

.35
.00
.87
.24
.69
.17

.25
.73
.02
.30
.40
.65
Chloride
July 13,
1.6
1.7
1.3
2.6
2.7
0.8
August 10
2.8
1.7
< 0.5
1.8
4.1
< 0.5
September
4.6
3.8
4.3
4.1
6.9
< 0.5
October 5
10.8
2.5
< 0.5
3.9
2.5
1.2
Noveiber
3.70
0.77
0.87
0.74
0.80
< 0.50
Noveiber
1.8
0.51
< 0.50
< 0.35
< 0.34
< 0.50
Nitrate
Jk Ammonia
Nitrite Nitrogen
Total
Phosphate
Ortho-
phosphite
Sulfate
1989 July 27, 1989
0.350
0.341
0.075
0.041
0.450
0.336
, 1989
0.165
0.286
0.027
< 0.010
0.153
0.133
7, 1989
0.936
1.11
0.849
0.323
1.02
0.479
, 1989 -
0.774
0.959
0.390
1.23
0.762
0.426
2, 1989
0.023
0.051
0.045
0.048
0.169
0.056
30, 1989
0.067
0.065
0.106
0.084
0.172
0.042
0.643
0.418
0.382
0.363
0.397
0.811
August 24,
0.517
0.078
0.061
0.022
0.763
0.160
- Septenber
0.949
1.72
0.206
0.977
8.04
0.384
October 19,
0.432
0.310
0.066
0.493
0.209
0.472
0.
0.
0.
0.
0.
0.
1989
0.
0.
0.
0.
0.
0.
062
054
170
096
084
040

118
015
160
066
236
056
< 0
0.
0.
0.
< 0.
0.

0.
0.
< 0-
< 0.
0.
< 0.
.002
019
016
009
002
014

043
115
002
002
036
002
8
7
10,
23.
15.
8.

4.
,0
2
,2
.1
8
2

3
5.7
2.
20.
24.
2.
2
8
3
8
21, 1989
0.
0.
0.
0.
0.
0.
1989
102
174
690
224
980
140

0.084
0.110
0
0
0
0
.150
.275
.094
.044
< 0.
< 0
0,
< 0
0.
< 0

< 0
< 0
< 0
< 0
< 0
< 0
.002
002
,293
,002
.016
.002

.002
.002
.002
.002
.002
.002
23.6
14.
75.
74,
3
9
.9
120
3

,8

286
30
21
40
.8
.8
.8
29.4
10
.9
Noveiber 16, 1989
0.023
0.051
0.045
0.048
0.032
0.056
December
0.067
0.036
0.106
0.038
0.035
0.042
0
0
0
0
0
0
.018
.019
.100
.066
.032
.008
< 0
< 0
0
< 0
< 0
< 0
.001
.001
.015
.001
.001
.001
5
3
3
2
3
0
.2
.2
.7
.6
.2
.9
14, 1989
0
< 0
0
0
0
0
.015
.001
.082
.026
.023
.007
< 0
< 0
0
< 0
< 0
< 0
.001
.001
.006
.001
.001
.001
3
3
2
2
3
1
.7
.2
.5
.4
.3
.5
                                     174
-------
Concentrations  of  Nutrients  in Atmospheric
Deposition  Samples Collected  in Tacoma
During  July to  December,  1989
                           Quality  Control - (Blank and Deposition Blank (DB) Data  ig/L

                                    Nitrate
                   Voluie               I     Ainonia     Total     Ortho-
Sanple               (L)     Chloride  Nitrite  Nitrogen   Phosphate  phosphite  Sulfate


Field Blank 8-10-89     -       < 0.6     0.276    0.078      0.015    < 0.001    < 0.5
Field Blank 11-30-89    -       < 0.5     0.014    0.013      0.021      0.001    < 0.5

Detection Liiit        -         0.5     0.010    0.005      0.001      0.001      0.5
                                                175
-------
Appendix C-10. Concentrations of Aliphatic Hydrocarbons and PCB Congeners in Deposition
Samples	                                	
                                        177
-------
Appendix C-10(a).
(ng/m2/day)	
Concentrations of Aliphatic Hydrocarbons in Deposition Samples (ng/L) and Atmospheric Deposition Rates
                                                        Sample Number
PCB Congener
n-C09
n-CIO
n-Cll
n-C12
n-C13
n-C14
n-C15
n-C16
n-C17
Pristane
n-C18
Phytane
n-C19
n-C20
n-C21
n-C22
n-C23
n-C24
n-C25
n-C26
n-C27
n-C28
n-C29
n-C30
n-C32
n-C34
n-C36
Total (ng/L)
Deposition
Rate (ng/mVday)
% Surrogate
Recovery
TM0713
ND
ND
ND
ND
ND
ND
ND
ND
160
ND
ND
ND
154
246
356
767
1,113
967
ND
ND
ND
ND
3,779
1,156
1,460
1,237
421
11,817

11,200

66
DTM0713
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
134
ND
ND
523
ND
1,221
978
ND
ND
3,088
1,143
1,525
1,289
980
10,881

14,400

50
SL0713
ND
ND
ND
ND
ND
ND
ND
ND
320
ND
206
ND
505
668
ND
ND
324
ND
ND
ND
ND
ND
747
3,540
ND
4,253
371
10,935

10,700

76
AS0713
ND
ND
ND
ND
ND
ND
ND
ND
161
ND
ND
ND
162
231
460
693
1,297
851
ND
ND
ND
ND
3,666
ND
ND
ND
1,131
8,653

10,200

55
TM1130
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
90
81
151
297
269
300
303
396
404
1,026
795
273
227
ND
4,613

25,400

28
SL1130
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
95
52
ND
137
110
134
105
125
129
803
ND
180
159
ND
2,029

13,600

26
MS 1130
ND
ND
ND
ND
ND
42
68
145
ND
200
934
1,654
3,562
ND
ND
ND
ND
ND
ND
96
733
547
ND
ND
64
170
114
8,329

34,803

144
AS1130
ND
ND
ND
ND
ND
ND
ND
ND
111
173
ND
576
772
1,269
350
363
ND
426
ND
ND
ND
ND
ND
ND
ND
ND
ND
4,041

27,400

84
DPS1130
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
165
86
177
227
286
ND
ND
ND
ND
1,450
ND
ND
404
146
2,941

17,000

51
RSI 130
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
132
ND
ND
ND
ND
165
127
170
189
1,288
ND
141
104
ND
2,315

17,400

42
-------
      Appendix C-10(b). Concentrations of PCB Congeners in Deposition Samples (ng/L) and Atmospheric Deposition Rates (ng/m2/day)
                                                             Sample Number
oo
o
PCB Congener
18
33
52
49
101
97
77
149
118
114
153
105
137
138
126
187
157
180
169
195
194
Total (ng/L)
Deposition Rate
(ng/m2/day)
% Surrogate
Recovery
TM0713 DTM0713 SL0713
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.3
2.3

2.2

68
6.0
ND
6.2
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
12.2

16

47
14.2
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
5.0
ND
ND
ND
9.1
ND
28.3

28

87
AS0713 TM1130 SL1130
29.2
17.5
38.8
21.1
41.7
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
166

196

53
ND
ND
ND
1.7
ND
ND
ND
ND
1.3
ND
ND
ND
ND
4.9
ND
ND
ND
ND
ND
ND
4.7
12.6

69

10
ND
1.8
ND
ND
ND
ND
ND
2.1
ND
ND
ND
ND
ND
5.5
ND
ND
ND
ND
ND
ND
ND
9.4

63

14
MS1130
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
7,889
ND
7,889

33,000

151
AS1130 DPS1130
ND
16.0
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
16

109

78
ND
ND
127.1
44.1
ND
ND
ND
ND
ND
ND
39.6
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
211

1,200

714
RSI 130
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.6
ND
ND
ND
ND
ND
ND
ND
ND
0.6

4.4

22
-------
Appendix C-ll.  PAH Deposition Data
                                      181
-------
Rate of  Atmospheric  Deposition  of PAHs at  Five Tacoma Sites  (ng/m^/day)
Con pound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anth racene
Crysene
Benzo (b)f 1 uoranthene
Benzo (k) f 1 uo ranthene
Benzo(a)pyrene
Indeno(l,2,3-cld)pyrene
D i benzo (a , h) anth racene
Benzo (g,h,i)perylene
CPAH 7/13
TM0713
ND
ND
ND
ND
ND
46.3
ND
123
114
23.7
94.6
63.4
18.9
41.6. .
32-1 (a)
81 ^fa
598
DTM0713
11.7
ND
ND
ND
ND
35.8
ND , .
98. 2 to
69.0
26.5
109
82.3 . .
8.49to
41.1
38.5
55.7
538
SL0713
ND
ND
16.7
56.0
60.1
854
226
3340
2260
834
3830 .
3240 to
2260
1280
2060
412
1960
21476
MS0713
ND
ND
ND
ND . .
36.3to
648
65. 3 W
1180
1180
396
1030.
696 to
150
568
471. .
118 to
514
6303
AS0713
ND
ND
ND
ND . .
g.eeto
141
24.7
507
377
141
601
377. .
188 to
130
130
36.3
165
2651
RS0713
ND
ND
ND
ND
ND M
36.9la'
ND
127
82.8
34.4
280
153 . .
34.4'
39. 5 to
35.7
ND
40.1
827

Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a) anth racene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k) f 1 uo ranthene
Benzo(a)pyrene
Indeno(ll2,3-c,d)pyrene
D i benzo (a , h) anth racene
Benzo(g,h,i)perylene
TM0727
13(b)
ND
ND
ND
ND
48.1
ND
71.7
54.3
21.5
76.8.
89.1 to
ND M
28. 7 to
22.5. ,
5.4to
24.6
DTM0727
ND
ND
ND
ND
ND
38.5
ND
109
93.8
27.6
190
117
48.1
44.5
45.7
9.25
79.3
SL0727
ll.7to
12.9
4.98
17.5
17.5
269
69.9
1090
753
216
1120.
928 to
511
323
498
113
538
MS0727
5.00
32.3
28.1
48.0
82.7
1401
108
289
2230
571
1740
1240. .
794 to
711
670
174
662
AS0727
18.8
ND
16.6
32.1
29.9
520
69.7
1220
874
432
830
663
487
531
443. .
165 to
976
RS0727
3. 13 to
ND
ND
ND , .
2.39to
46.0 . .
9.93to
202
129
57.0
460
221
86.4
44.1
49.6
19.4
53.3
CPAH 7/27
455
         764
6089
                                                    9081
6601
1322
                                          183
-------
Atmospheric  Deposition, cont'd
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a)anth racene
Crysene
Benzo (b)f 1 uoranthene
Benzo (k) f 1 uoranthene
Benzo (a) py rene
Indeno (1 , 2 , 3-c , d) py rene
D i benzo (a , h) anth racene
Benzo (g,h, i)perylene
CPAH 8/10
TM0810
ND
ND
ND
ND
ND
72.0
ND
170
144
36.7
131
95. 6^
41.9
51.l(a)
43.2
11.0
60.2
785
DTM0810
ND
ND
ND
ND
ND
83.7
ND
208
151
54.3
176
115 M
58.8laJ
67.8^aJ
56.5
15.8
61.0
964
SL0810
248(a)
19.0(a)
ND
29.1
33.5^aJ
539
90.4
1750
1400
510
1900
1600 W
962
714
875
219
933
10863
MS0810
62.1
25.9
17.1
25.9
36.2
621
64.7
1580
1190
388
1290
880
220
518
492
127
492
7177
AS0810
ND
15.2'aJ
23.2
60.7
62.5
1430
161
4280
3120
1520
2950
2410
1700
1870
1430
339
1160
20779
RS0810
11.2W
ND
ND
ND
ND
98.1
8.8BW
407
263
95.7
765
407
20. 3 W
95.7
95.7
23. 9 (a'
117
2290
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anth racene
Crysene
Benzo (b) f 1 uoranthene
Benzo (k) f 1 uoranthene
Benzo(a)pyrene
Indeno (1,2, 3-c , d) py rene
Di benzo (a , h) anthracene
Benzo (g,h, i)perylene
TM0824
150
ND
ND
ND
20.2
404
27.7^aJ
1320
940
165
1081
611
291
188
132
61.1
183
SL0824
94.2
21
ND
32.1
41.6
600
111
2480
1800
557
2660
1880
1071
685
771
360
1028
MS0824
29 (a)
ND
ND
ND,
29W
530
61
1473
1316
491
1375
1021
491
609
452
130 W
471
AS0B24
43(a)
ND
62
124
105
2600
260
9286
5633
2476
9905
5943
2786
2662
2167
619
1857
RS0824
92.3
ND
ND
23.1
17. 3^
358 , .
IS.iW
1130
669
242
2310
1390
ND
139
139
72.7
196
CPAH 8/24
4972
                  13292
7830
                                      43333
                                                6287
                                           184
-------
Atmospheric  Deposition,  cont'd
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anth racene
Crysene
Benzo (b)f luoranthene
Benzo (k)f luoranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Di benzo (a , h) anthracene
Benzo (g , h, i)pery lene
CPAH 9/7
TM0907
ND
ND
ND
ND
ND
217.
25 C«)
366
244
96
795
450
ND
64 W
89, x
25 W
69
2176
DTM0907
22.0
ND
ND
ND
ND
132 , .
8.10W
387
266
88.1
881
681
ND
74.9
67.8
30.8
96.9
2462
SL0907
48.9
35.9
22.9
61.3
74.3
1110
248
5460
3710
1180
5880
6000
ND
1480
1550
681
1790
27723
MS0907
*2, .
42 (a)
ND
25.3
41.3
553
41.3
1400
1130
347
1330
733
433
367
253
93.3
313
6399
AS0907
64W
68 W
101
232
241
6250
63
20833
15179
8333
38690 W
22321
10417
8929
7440
1875
6250
140268
RS0907
22
ND
ND
15.5
9.04
156 , .
18. iW
1046
646
219
1550
981
ND
121
114
47.8
142
4867
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anth racene
Crysene
Benzo (b)f 1 uoranthene
Benzo (k) f 1 uoranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
D i benzo (a , h) anth racene
Benzo (g, h, i)pery lene
TM1102
371
ND
ND
ND
ND
608
ND
1013
675.
101 W
669:
466 w
NDrai
101 w
65.5
ND
101
SL1102
588
ND
ND
93.1. .
58. 8 W
637
ND
206
1470
436
1810
1670
ND
397
333
167
471
MS1102
612
ND
ND
45.6
ND
306 , .
39.7^)
958
730
214
653, ,
429 '
228 W
224
146 ,
59. 3 l^
233
AS1102
84«
ND
90
257
160 ^'
3618
390
12525
8350
3618
9046
5984
3479
3479
2435,
578 w
2018
RS1102
514
ND
ND
ND
ND
793
ND
1260
818
143
843
379
ND
f-\
37. 9 W
ND
84.3
CPAH 11/2
3192
                                                     3874
                                     51513
3565
                                           185
-------
Atmospheric Deposition, cont'd
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo (a) anthracene
Crysene
Benzo (b)f 1 uoranthene
Benzo (k) f 1 uo ranthene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Dibenzo (a, h) anthracene
Benzo (g,h, i)perylene
CPAH 11/16
TM1116
211
ND
25.8
54.1
51.5
1160. .
25oo
3090
1620
386
2580
1420
ND
131
85.0
54.1
90.2
9457
SL1116
261
55.3
233
166
51.4
593
63.2
2370
1540
391
1820
1380
ND
0
205
86.9
253
8046
MS1116
173
ND
ND
ND
ND
186
ND
1150
974
217
974
753
0
195
168
58
297
4785
AS1116
166
44
124
171
119
2320
304
21300 W
12100 W
3040 rw
11600W
8840 V)
ND
1740
1080
497
1080
61263
RS1116
395
57. 6 (O
ND
ND
ND
115
ND
1153
576
160
1064
665
ND
Ulla;
89
38.6^'
124
3979
Compound
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a)anthracene
Crysene
Benzo (b) f 1 uoranthene
Benzo(k)f 1 uoranthene
Benzo(a)pyrene
Indeno (1,2, 3-c , d) py rene
Dibenzo (a, h) anthracene
Benzo (g,h, ijpery lene
CPAH 11/30
TM1130
121(0
ND
ND
138
99
2147
61
6057
3249
1211
9911
5506
ND
534
512
226 W
451
27656
MS1130
501
543
752
1130. .
261 W
3090
1290
4090
3220
1960
3170
2000
1590
1460
1130
1090
1170
12605
SL1130
87(a)
ND
141
168. .
87 W
1143
ND
3094
1951
639
3161
1749
592
444
430
12l(a)
424
20882
DAS1130
209 W
ND
ND
290
284
8108
284
25483
13900
4633
26642
17954
ND
2433
2143
869 W
1795
95852
AS1130
678
63. 8 (a
142
387
516
10200
285
22400
11500
2850
17000
9500
ND
1420
814
448
882
66814
RS1130
. 256
> ND
ND
ND
ND
286
ND
655
444
75.3
467
218
ND
27.1 a
21 s'a'
ND'
34.6
1943
                                      186
-------
Atmospheric Deposition,  cont'd
Compound
TU1214
SL1214
MS1214
AS1214
RS1214
Naphthalene
Acenaphthalene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fl uoranthene
Pyrene
Benzo (a) anth racene
Crysene
Benzo (b)f 1 uoranthene
Benzo (k) f 1 uoranthene
Benzo(a)pyrene
Indeno (1 , 2, 3-c , d) py rene
D i benzo (a , h) anth racene
Benzo (g,h(i)pery lene
CPAH 12/14
260
ND
ND
ND
ND
1736
ND
6171
4050
1736
10607
7136
ND
791
665
289 ^a'
617
32063
ND
ND
ND
ND
ND
812
ND
5831
4281
1624
8857
5831
ND
886
723
295
886
29214
143
30
ND
44
65
1050
66
3620
2670
1050 K\
6330 W
2290
914 W
524
419
209
571
17683
203
ND
35
84
114
2170
326...
19000 W
12600 W
5970 W
12800 W
14900 
-------
Appendix C-12.  Quality Control for Chemical Analysis
                                         189
-------
Appendix C-12(a).  Concentrations of PAH Compound's in Field Blanks
Filter"' fae/m3}
COMPOUND
Naphthalene
Acenaphthelene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a)anthracene
Chrysene
Benzo(b)fluoranthene
Benzo(k)fluoranthene
Benzo(a)pyrene
Indeno(l ,2 ,3-c,d)pyrene
Dibenzo(a,h)anthracene
Benzo(g,h,i)perylene
% Surrogate Recoveries
d8 Naphthalene
dlO Acenaphthene
d!2 Perylene
1
0.25
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND

31
48
95
2
0.33
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND

23
31
59
3
0.17
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND

24
42
93
PUF fne/m3)
1
1.6
1.6
1.9
2.0
ND
2.0
2.0
2.4
2.2
2.3
2.3
2.1
2.0
2.1
1.8
2.1
2.0

16
62
93
2
1.5
1.6
1.9
2.0
ND
2.1
2.0
2.4
2.2
2.3
2.3
2.1
2.1
2.2
1.8
2.1
2.0

16
44
91
3
1.2
1.4
1.6
1.8
ND
2.0
2.0
2.5
2.3
2.6
2.4
2.3
2.2
2.8
2.1
2.3
2.2

11
53
104
Water Cne/D
1
ND
ND
ND
ND
ND
9.6(b)
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
7 3®

15
31
75
2
ND
ND
ND
ND
ND
ND
ND
12o»
350"
ND
ND
ND
ND
9.5
7.7
ND
490.)

20
29
83
3
ND
ND
ND
ND
ND
ND
ND
80°"
10°°
ND
ND
ND
ND
ND
ND
ND
ND

14
21
91
(a) Approximately of 1,000 m3 of air sampled.
(b) Numbers suspect because ion ration not within specified range.
                                          191
-------
Appendix C-12(b).  Method Detection Limits for PAH Compounds in Filters, PUFs, and
Water
COMPOUND
Naphthalene
Acenaphthelene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benz(a)anthracene
Chrysene
Benzo(b)fluoranthene
Benzo (k) fluoranthene
Benzo (a)pyrene
Indeno(l ,2,3-c,d)pyrene
Dibenzo(a,h)anthracene
Benzo (g ,h , i)pery lene
Filter
ng/m3
0.20
0.22
0.12
0.11
0.11
0.098
0.16
0.12
0.12
0.18
0.15
0.27
0.15
0.27
0.20
0.26
0.20
PUF
ng/m3
0.086
0.096
0.051
0.048
0.048
0.042
0.069
0.053
0.050
0.077
0.063
0.12
0.065
0.11
0.84
0.11
0.085
Water
ng/L
19
14
17
13
13
8.1
8.3
18
17
28
23
29
40
34
28
18
20
                                       192
-------
Appendix C-12(c).  Percent Spike Recoveries for PAH Compounds on Blank Filters, Blank
PUFs and Blank Water
COMPOUND
Naphthalene
Acenaphthelene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benz(a)anthracene
Chrysene
Benzo(b)fluoranthene
Benzo(k)fluoranthene
Benzo(a)pyrene
Indeno(l ,2,3-c,d)pyrene
Diben2X)(a,h)anthracene
Benzo(g,h,i)perylene
% Surrogate Recoveries
d8 Naphthalene
dlO Acenaphthene
d!2 Perylene
Filter"'
fl.S ng/nft
1 2
61
39
52
50
NS
51
50
72
65
65
78
78
72
56
65
72
72

40
56
89
51
36
48
48
NS
50
50
72
65
64
72
78
72
57
65
72
65

35
50
88
PUF("
(2.5 ne/m3)
1
64
64
76
80
NS
80
80
96
88
92
92
84
80
84
72
84
80

16
62
93
2
60
64
76
80
NS
84
80
96
88
92
92
84
84
88
72
84
80

16
44
91
3
48
56
64
72
NS
80
80
100
92
104
96
92
88
112
84
92
88

11
53
104
Water
(500 ne/U
1
44
50
58
64
NS
72
72
94
90
118
112
120
112
114
118
130
106

15
31
75
2
38
40
46
44
NS
48
36
58
54
74
84
88
82
66
68
56
70

20
29
83
3
42
44
54
46
NS
54
40
62
62
86
102
106
102
76
84
62
86

14
21
91
(a) Assumed 1,000 m3 air samples.

NS = not spiked
                                       193
-------
Appendix  C-12(d).    Concentrations  of  PAH  Compounds  in  NIST  SRM  1649
(Urban Dust) (ng/g)
Compound
Naphthalene
Acenaphthelene
Acenaphthene
Fluorene
Dibenzothiophene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benz(a)anthracene
Chrysene
Benzo (b) fluoranthene
Benzo (k) fluoranthene
Benzo (a)pyrene
Indeno(l,2,3-c,d)pyrene
D ibenzo (a ,h) anthracene
Benzo(g ,h , i)pery lene
% Surrogate Recoveries
d8 Naphthalene
dlO Acenaphthene
d!2 Perylene
Certified Value Non-Certified
This Study +. uncertainty Values
140
ND
110
180
180
4,000
480
7,200 7,100 + 500
6,100
2,500 2,600 + 300
4,800
6,800
2,500
2,700 2,900 + 500
2,700 3,300 + 500
560
3,300 4,500 ±1,100

20
50
80


4,500


6,300

3,700
6,200
2,100


410





                                      194
-------
Appendix  C-12(e).   Method  Detection Limits  for PCB Congeners  in Air and Deposition
Samples
CONGENER
18
33
52
49
101
97
77
149
118
114
153
105
137
138
126
187
157
180
169
195
194
PUF
ng/m3xlO'3
5.94
5.40
5.40
4.60
4.60
1.53
4.06
5.40
5.36
9.40
4.95
5.36
6.54
4.95
4.95
5.36
5.86
6.14
5.36
8.68
6.29
Filter
ng/m3
0.020
0.018
0.018
0.015
0.015
0.005
0.014
0.018
0.018
0.031
0.016
0.018
0.022
0.016
0.016
0.018
0.020
0.020
0.018
0.029
0.021
Water
ng/LxlO4
5.94
5.40
5.40
4.60
4.60
1.53
4.06
5.40
5.36
9.40
4.95
5.36
6.54
4.95
4.95
5.36
5.86
6.14
5.36
8.68
6.29
                                        195
-------
Appendix C-12(f). Method Detection Limits for Aliphatic Hydrocarbons in Air and Deposition
Samples
COMPOUND
C9
CIO
Cll
C12
C13
C14
CIS
C16
C17
Pristane
CIS
Phytane
C19
C20
C21
C22
C23
C24
C25
C26
C27
C28
C29
C30
C32
C34
C36
PUF
ng/m3
0.508
0.408
0.209
0.240
0.249
0.259
0.264
0.283
0.278
0.285
0.292
0.302
0.313
0.200
0.301
0.318
0.324
0.294
0.232
0.275
0.228
0.340
0.204
0.249
0.302
0.773
1.128
Filter
ng/m3
1.693
1.360
0.697
0.800
0.830
0.863
0.880
0.943
0.927
0.950
0.973
1.007
1.043
0.667
1.003
1.060
1.080
0.980
0.773
0.917
0.760
1.133
0.680
0.830
1.007
2.577
3.760
Water
ng/L
0.051
0.041
0.021
0.024
0.025
0.026
0.026
0.028
0.029
0.028
0.029
0.030
0.031
0.020
0.030
0.032
0.032
0.029
0.023
0.028
0.023
0.034
0.020
0.025
0.030
0.077
0.113
                                        196
-------
Appendix C-12(g).  Spike Recovery for Aliphatic Compounds in Blank Filter


          COMPOUND	ng/mL SPIKE           % RECOVERY
n-C09
n-CIO
n-Cll
n-C12
n-C13
n-C14
n-C15
n-C16
n-C17
Pristane
n-C18
Phytane
n-C19
n-C20
n-C21
n-C22
n-C23
n-C24
n-C25
n-C26
n-C27
n-C28
n-C29
n-C30
n-C32
n-C34
n-C36

910

679

969
1022
1595


1191


1368

1844

4759



1863

1748
1671

1030

61

45

65
68
106


79


91

123

159



124

116
111

69
            % Surrogate
             Recovery                                     78
                                      197
-------
Appendix C-12(h).  Comparison Results for Fe, Ca, and K in Three Filters Analysed by X-
ray Fluorescence (XRF) and Atomic Absorption (AA)
Sample
AS 891115


RS 891211


AS 890907


Element
Fe
Ca
K
Fe
Ca
K
Fe
Ca
K
XRF
fig/cm2
11.34
21.29
5.56
7.25
1.48
3.25
37.50
48.3
13.07
AA
fig/cm2
11.54
21.20
5.66
6.96
1.68
3.84
37.5
49.0
9.8
                                       198
-------
Appendix C-12(i). Quality Control Results for Analyses of Metals in Deposition Samples



                                       itg/L
Sample
SLRS Rep. 1
Rep. 2
Certified Value
±0.08
1643b Rep. 1
Rep. 2
Certified Value

Field BLK 1
Field BLK 2
Field BLK 3
Mean BLK
Urban Dust (0.025
1648 Rep. 1
1648 Rep. 2
1648 Rep. 3
Mean
Certified Value
% Recovered
Matrix Spike
Field BLK 2
Matrix Spike
% Recovery
Matrix Spike
Field BLK 1
Matrix Spike
% Recovery
MDL
As
0.83
0.73
0.55
±0.04
NA
NA
None
±0.4
0.02
0.01
<0.01
0.01
g/100 mL)
118
103
109
110
115
96

0.01
11.58
116

0.02
12.6
124
0.01
Cr
0.31
0.33
0.36
±0.3
18.76
20.55
18.6
±0.4
0.67
<0.27
0.31
0.41

81.1
90.4
90.7
87.4
403
22

<0.27
20.40
102

0.67
21.64
105
0.27
Cu
3.16
3.20
3.58
±0.23
21.8
22.7
21.9
±2
<0.32
<0.61
2.49
<1.14

621
596
647
621
609
102

<0.61
46.6
93

<0.32
46.3
93
0.52
Mn
1.71
1.60
1.77
±0.06
32
28
28
±3
0.15
1.37
<0.04
0.52

773
717
749
746
860
87

1.37
110
109

0.15
125
125
0.05
Ni
1.39
1.13
1.07
±0.01
54
44
49
±0.7
<1.1
<1.0
<1.0
<1.06

139
125
119
128
82
156

<1.0
29.0
112

<1.1
29.5
114
1.04
Pb
0.67
0.47
1.06
±0.20
24.8
27.0
23.7
±2
<0.33
0.59
0.50
0.49

6,676
6,156
6,377
6,403
6,550
98

0.59
62.5
124

<0.33
59.4
118
0.33
Zn
<1.6
<1.6
1.34

63
59
66

<1.6
9.6
<1.6
<4.3

1,128
1,128
1,128
1,128
4,760
24

9.6
109
99

<1.6
112
110
1.6
                                          199
-------
Appendix D.  Emission Inventory
      D-l.  PSAPCA Point Source Metal and PAH Data	203
      D-2.  Source Profile Information	211
      D-3.  Kaiser Emission Data	243
      D-4.  Simpson Tacoma Kraft Source Test  	247
      D-5.  Area Source Emission Calculations	265
                                    201
-------
Appendix D-l. PSAPCA Point Source Metal and PAH Data
                                   203
-------
    Appendix D-l. PSAPCA Tbxic Emission Inventory
    REG I    SOURCE
METALS
                           TOXICS INCLUDING
LBS/1988    POLVCYCLIC AROMATIC HYDROCARBONS (PAHs)
LBS/1988
    13511     Lianga Pacific Inc.
    12593    U.S. Oil & Refining
Chromium
Manganese
Nickel
            Toluene

      29    Ethjibenzene
      17    Formaldehyde
     588    POM
            Trichloroethane
   18,810

     190
     139
       1
     300
to
g
    16321    Auto Warehousing Co.
    10068    Sierra Sandblasting and Painting Co.
ND
    10911    Girard Custom Coalers
    10076    Puget Sound By-Products Company
    14071     Lone Star Northwest
ND

ND
            ND

            Butoxyethyl Acetate
            Ethylbenzene
            Mineral Spirits
            Naphtha VM&P

            Acetone
            Butyl Acetate[1690]
            Butyl Alcohol[210]
            Hexane[429]
            Isopropyl Alcohol
            Methanol (Methyl Alcohol) [36]
            Methyl Ethyl Ketone (Butanone)[160J
            Methyl Pentanone (Methyl Isobutyl Ketone) [280]
            Naphtha VM&P
            Toluene[51]
            Xylene[59]

            ND

            ND
                                                                                         16
                                                                                          8
                                                                                        143
                                                                                       3,959

                                                                                       3,388
                                                                                       4,655
                                                                                      12,927
                                                                                      83,871
                                                                                       5,592
                                                                                       3388
                                                                                      13,414
                                                                                      57,042
                                                                                       8,027
                                                                                     124^83
                                                                                     116,750
    ND = No Data
-------
  REG#    SOURCE
METALS
   13461     Kaiser Aluminum
   10037
Aluminum Oxide
Fluorides
Nickel
to
o
ON
  12048    Reichhold Chemicals
  11866    Pennwalt Inorganics
  12609    U.S.G. Interiors
  12429    Tacoma Boatbuilding Company
ND
ND

Chromium
Lead
LBS/1988
862,000
223,600
4


















513
855




TOXICS INCLUDING
POLYCYCLIC AROMATIC HYDROCARBONS (PAHs)
Acenaphthalene
Acenaphthene
Anthracene
B enzo [a] Anthracene
Benzo[a]Pyrene[.0006]
Chrysene
Cyanide Compounds
Fluoranthene
Fluorene
Formaldehyde[.77]
Hydrogen Fluoride[3.4]
Naphthalene[14.0]
Phenanthrene
Phenol[52]
Pyrene
Acetone
Ethanol
Methanol
Chlorine
HCI
ND
Butyl Alcohol [210]
Methanol (Methyl Alcohol) [36]
Methyl Amyl Ketone [560]
Methyl Ethyl Ketone (Butanone) [160.0]
Naphtha
Xylene[59]
LBS/1988
9,120
124,280
1,560
7,380
6,180
12,000
72
61,400
36,200
10
51,000
57,800
114,160
43,760
24.65
48,432
34,409
50,860
74
15

4,010
120
2,005
12429
1,441
4,010
 ND = No Data
-------
REG# SOURCE
6330 Tacoma Public Works Sewer Utility



10340 Buffelen Woodworking




1 1820 Continental Lime Inc.
21432 General Metals of Tacoma
O 10016 Domtar Gypsum
10073 Simon Joseph & Sons
16043 Woodworth & Co.

13828 Sound Refining


10074 Tacoma Port Facilities
12230 Pacific N.W. Terminals
METALS
ND



Manganese




ND
ND
ND
ND
ND

Chromium
Manganese
Nickel
ND
Changed from I
TOXICS INCLUDING
LBS/1988 POLYCYCLIC AROMATIC HYDROCARBONS (PAHs)
Dichloroethylene
Tetrachloroethane
Tetrachloroethylene
Trichloroethjlene
21,184 Acetaldehyde
Dioxins
Formaldehyde
Phenol
POM
ND
ND
ND
ND
Butraldehyde
Formaldehyde
4 Formaldehyde
2 Ammonia
71
ND
raining No PAHs
LBS/1988
24
237
6
164
5,084
1
10,168
42,368
85




304
2,537
17
569



12315     Commencement Bay Mill (Simpson)
residual oil to natural gas
(1987)—No metals

ND
ND
ND = No Data
-------
to
o
oo
REG# SOURCE
11053 Occidental Chemical



123 17 Simpson Tacoma Kraft Co.





10463 Coastcraft, Inc.
1 1974 Puget Sound Plywood




10995 Brandrud - Harmon Division












TOXICS INCLUDING
METALS LBS/1988 POLYCYCLIC AROMATIC HYDROCARBONS (PAHs)
ND Ammonia
Chlorine
Chloroform
Methylene Chloride
Chromium 60 Acetaldehyde[.45]
Manganese 80,200 Chloroform[.043]
Nickel 540 Dioxins[000]
Total Reduced Sulfur Formaldehyde[.77]
(TRS) Compounds 532,600 Phenol[52]
POM (Polycyclic Organic Matter)
ND ND
Manganese 69,000 Acetaldehyde
Dioxin
Formaldehyde
Phenol
POM
Manganese 600 Acetaldehyde
Acetone
Butyl Alcohol
Formaldehyde
Hexane
Isobutyl Acetate
Isopropji Alcohol
Methanol (Methyl Alcohol)
Methyl Ethyl Ketone (Butanone)
Naphtha VM&P
Phenol
POM (Polycyclic Organic Matter)
Toluene
LBS/1988
21,220
1,464
13
601
19,260
356,000
3
38,780
160,400
320

16,500
26
33,128
138,000
276
144
165
165
288
1,307
462
165
165
1
165
1,200
2
3
   ND = No Data
-------
REG#
10099
2424
12424
12716
21085
12444
11583
14242
SOURCE
Yale Industry
(American Manufacturing)
Monitor Inc.
Atlas Foundry & Machine
West Coast Door
Tacoma Public Works
(asphalt production)
TAM Engineering Corp.
NaUey's
American Reinforced Plastics
TOXICS INCLUDING
METALS LBS/1988 POLYCYCLIC AROMATIC HYDROCARBONS (PAHs)
ND Butyl Alcohol
Ethoxyethji Acetate
Methyl Ethyl Ketone
Toluene
Xjiene
Nickel 2 Hexane
Methyl Ethyl Ketone
Toluene
ND ND
Manganese 5,000 Acetaldehyde
Formaldehyde
Phenol
POM
Butraldehyde
Formaldehyde
Isobutyraldehyde
Naphtha
Toluene
Xylene
ND ND
ND Acetone
Methyl Ethyl Ketone
Styrene
LBS/1988
196
1398
921
905
823
3,515
2,589
2,126

1^00
2,400
10,000
20
20
168
11
49,738
943
481

21,780
2,680
54,485
ND = No Data
-------
Appendix D-2.  Source Profile Information
                                       211
-------
Dr. Ted Harrison
WYNDSoft, Inc.
6333 77th Avenue SE
Mercer Island, Washington 98040

September 13,  1989                 Re: Tacoma Tideflats Source
                                       Profiles

Dear Ted,

     Enclosed  is the information that you and Naydene requested

     1. A listing  (Table 1) of the Tacoma Tideflats sources
     incorporating notes provided by PSAPCA on the nature of
     the emissions from each of the source types. The
     column notes the associated source emission profile.

          - The PACS profiles were developed during the
          Portland Aerosol Characterization Study. The
          PACS number (e.g. PACS 3173) refers to Table
          3.1.7.3 of J.G Watson^Ph.D. Thesis Chemical
          Element Balance Receptor Model Methodology For
          Assessing the Sources of Fine and Total
          Suspended Particulate Matter in Portland.
          Oregon, Oregon Graduate Center, February,
          1979.

          - The SCAQMD profiles were obtained from the
          South Coast Air Quality Management District
          Source Profile Project.  SCAQMD Profile 51
          refers to source number 51 in the project's
          listing of PM^o emission profiles as
          referenced in the South Coast Air Quality  -
          Management District Source Library, NBA, Inc.
          November, 1987.

          - The numbered profiles were obtained from
          either the US EPA Receptor Model Source
          Composition Library (US EPA 450/4-85-002,
          November, 1984) or the soon to be released
          Pacific Northwest Source Profile Library.
          Oregon Department of Environmental Quality,
          September, 1989.

     2. Table 2 is a listing of the chemical species included in
the PNW Source Profiles. You will need this listing to decode the
organic compound abbreviations found in the hardcopy and ASCII
profiles. Note that PAH compounds found in the source profiles are
footnoted.

     3. Hardcopy listings of each of the profiles found in the
ASCII file.  I have included these in the event that you wish to
use them in project reports.
-------
     4. A floppy disk (DOS 3.3 format, DD/DS 360Kb) containing the
profiles in ASCII format (PROFILES.ASC).  The first field contains
a profile number (1 to 19)  followed by the weight percent of the
PM10 faction for the chemical specie found in the third field. The
fourth field is the source profile number from which the data was
taken.

     I hope this information is helpful to you. Please advise if
you need further clarification or assistance.


Sincerely,
John Core
11520 SW Clifford Street
Beaverton, Oregon 97005
Enclosures

cc: Naydene Maykut, Puget Sound Water Quality Authority
-------
                                           Table  1
TACOMA TIDEFLATS SOURCE PROFILES

 NO. FACILITY                 SOURCE
                         N/A = NOT AVAILABLE

                         COMMENTS
  15 LONE STAR NORTHWEST
  16

  17 WEST COAST DOOR
  18

  19 CONTINENTAL LIME

  20 US OIL & REFINING
  21

  22 CONTINENTAL GRAIN
CEMENT FUGITIVES
CEMENT KILN

CYCLONES
HOGGED FUEL BOILER

LIME KILN
OIL-FIRED BOILER
ASPHALT HEATERS

GRAIN FUGITIVES
                         KILN NO LONGER IN USE

                         RAW WOOD FIBER
                         NO PLY TRIM IN FUEL
                         RESIDUAL OIL FIRED
                         DISTILLATE OIL
  23 GENERAL METALS OF TACOMA SCRAP HANDLING FUGITIVES
  24 COASTCRAFT INC

  25 DOMTAR GYPSUM

  26 USG INTERIORS
  27
WOOD CYCLONES

GYPSUM FUGITIVES

CURING OVENS
3 CUPOLAS
                                                       RAW WOOD  FIBER
                                                                                PROFILE NO.
1 SIMPSON TACOMA KRAFT CO.
2
3
4
5 KAISER ALUMINUM
6
7 WOODWORTH & CO.
8
9 BUFFELEN WOODWORKING
10
11
12 PUGET SOUND PLYWOOD
13
14
KRAFT RECOVERY
LIME KILN
SMELT TANK
HOGGED FUEL BOILER
POTLINES
ALUMINA HANDLING
ASPHALT BATCH PLANT
ROCK CRUSHING
VENEER DRIER
HOGGED FUEL BOILER
CYCLONES
3 VENEER DRIERS
HOGGED FUEL BOILER
CYCLONES



NO PLY TRIM IN FUEL




SOURCE NOT OPERATING
NO PLY TRIM IN FUEL
RAW WOOD FIBER
STEAM HEATED
BURNING PLY TRIM
RAW WOOD FIBER
23104
23202
N/A
12706
29102
PACS 3173
PACS 3112
PACS 3111
	
12706
22203
22302
12707
22203
  28 TACOMA PORT FACILITY     ALUMINA FUGITIVES

  29 COMMENCEMENT BAY MILL    WOOD CYCLONE

  30 CANYON SAND & GRAVEL     SOIL FUGITIVES

  31 SCOFIELD GEORGE CO       CEMENT PRODUCT.
                         CASTI RON  CUPOLA  PROFILE
                         RAW WOOD FIBER
                         CEMENT FUGITIVES
  32 SOUND REFINING
  33
BOILERS-DISTILATE OIL
BOILERS-RESIDUAL OIL
SCAQMD 51


   22203
   12706

   23202

   13502
PACS 3132

   21401

PACS 3193

   22203

   27601

     N/A
   28202

PACS 3173

   22203

   41302

SCAQMD 51

PACS 3132
   13502
                                                 215
-------
TACOMA TIDEFLATS SOURCE PROFILES





 NO. FACILITY                 SOURCE
N/A = NOT AVAILABLE





COMMENTS
                                                                                PROFILE NO.
34 CANYON READY MIX
35 PACIFIC INTER'L PIPE
36 KAISER ALUMINUM & CHEM.
37 LIANGA PACIFIC
38
39 OCCIDENTAL CHEM.
40 HARMON DIVISION
41 PACIFIC NW TERMINALS
42 TACOMA PUBLIC WORKS
43 NALLEYS FOODS
44 TACOMA BOATBUILDING

CONCRETE BATCH PLANT
CEMENT PRODUCTS BAGGING FUGITIVES
ALUMINA FUGITIVES
HOG FUEL BOILER NOT BURNING PLY TRIM
LUMBER PROCESSING WOOD FIBER
H2 FIRED BOILER
WOOD DUST FUGITIVES
OIL BOILERS SOURCE NOT OPERATING
ASPHALT BATCH PLANT
FUEL COMBUSTION NATURAL GAS
SAND BLASTING FUGITIVES
PAINT SPRAY FUGITIVES
SCAQMD 51
SCAQMD 51
PACS 3173
12706
22203
N/A
22203
	
PACS 3112
PACS 313
N/A
25403
  45 SIERRA SANDBLASTING
                              SAND BLASTING FUGITIVES
                                                                                     N/A
                                                 216
-------
    Species
  Table 2: Chemical Species Codes



Code Species Name             Method *
F -
NA+
MG+
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
OC
EC
S04=
N03-
CO3
NH4+
HPO4-
K+
CL -
9 W/S FLORIDE
11 W/S SODIUM
12 W/S MAGNESIUM
13 ALUMINUM
14 SILICON
15 PHOSPHORUS
16 SULFUR
17 CHLORINE
19 POTASSIUM
20 CALCIUM
22 TITANIUM
23 VANADIUM
24 CHROMIUM
25 MANGANESE
26 IRON
27 COBALT
28 NICKEL
29 COPPER
30 ZINC
31 GALLIUM
33 ARSENIC
34 SELENIUM
35 BROMINE
37 RUBIDIUM
38 STRONTIUM
39 YITTRIUM
40 ZIRCONIUM
42 MOLYBDENUM
46 PALADIUM
47 SILVER
48 CADMIUM
49 INDIUM
50 TIN
51 ANTIMONY
56 BARIUM
57 LANTHANUM
80 MERCURY
82 LEAD
201 ORGANIC CARBON
202 ELEMENTAL CARBON
203 W/S SULFATE
204 W/S NITRATE
205 CARBONATE
206 W/S AMMONIUM
207 W/S PHOSPHATE
208 W/S POTASSIUM
209 W/S CHLORIDE
1C
AAS
AAS
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
XRF
TOR
TOR
1C
1C
TOR
AC
1C
AAS
1C
Pacific Northwest Source Profile Library Appendix



                              217
                                               Pag
-------
    Species
  Table  1: Specie Codes, Continued

Code Species Name             Method *
FLOR
CARB
PHEN
ANTH
ACRI
DIBE
FLUO
PYRE
BECP
CHRY
RETE
BENB
BEBF
BEEP
BAP
PERY
INDE
BEGP
DIAA
TETR
PENT
HEXA
KEPT
OCTA
NONA
TRIA
1761 FLUORENE **
1671 CARBAZOLE
1781 PHENANTHRENE **
1782 ANTHRACENE **
1791 ACRIDINE
1841 DIBENZOTHIOPHENE
2021 FLUORANTHENE **
2022 PYRENE **
2281 BENZO(C) PHENANTHRENE
2282 CHRYSENE **
2341 RETENE
2342 BENZO(B)NAPTHOL(1,2 D)
2521 BENZO(B+K) FLUORANTHENE **
2522 BENZO(E) PYRENE **
2523 BENZO (A) PYRENE **
2524 PERYLENE
2761 INDENO (1,2, 3 -C,D) PYRENE **
2762 BENZO (GHI) PERYLENE
2781 DIBENZf A, H) ANTHRACENE **
3381 TETRACOSANE
3521 PENTACOSANE
3661 HEXACOSANE
3801 HEPTACOSANE
3941 OCTACOSANE
4081 NONACOSANE
4221 TRIACOSANE
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
CG/MS
* Note: AC = Automated Colorimetry
     AAS = Atomic Absorption Spectroscopy
       XRF = X-ray fluorescence
        1C = Ion Chromatography
     GC/MS = Thermal Desorption Gas Chromatography/
           Mass Spectroscopy
       W/S = Water Soluble

   Organics
   ** = PAH Compounds
   Tetracosane = C
                  24
   n-
   Pentacosane = C25 n-
   Hexacosane  = C26 n-
   n-
   Heptacosane =
   Octacosane  = C28 n
   Nonacosane  = C29 n
   Triacosane  = C30 n
alkanes
alkanes
alkanes
alkanes
alkanes
alkanes
alkanes
Pacific Northwest Source Profile Library Appendix
                                               Page  7
                              218
-------
SOURCE: Distillate Oil Furnace                     Profile:PACS 3132

DESCRIPTION: Portland Distillate Oil Furnace profile from PACS.

SPECIES    FINE   +-  UNCERT   COARSE  +-  UNCERT    PM-10  +-   UNCERT
F -
CL -
N03-
HP04-
S04=
NH4+
NA+
MG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
0.0000 +-
NM +-
1.0000 +-
NM +-
13.2000 +-
NM +-
0.3200 +-
0.0000 +-
NM +-
18.0000 +-
17.8000 +-
NM +-
0.3100 +-
0.2700 +-
NM +-
6.9300 +-
1.2000 +-
0.0180 +-
0.5000 +-
0.0000 +-
0.0050 «•-
0.0000 +-
0.0140 +-
0.1200 +-
NM +-
0.0090 +-
0.1700 +-
0.0290 +-
NM +-
NM +-
NM +-
0.0260 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +•
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.5400 +-
0.2000
NR
0.5000
NR
8.7000
NR
0.2300
2.0000
NR
5.6600
22.9000
NR
0.2100
0.3200
NR
2.6200
0.9000
0.0130
0.5500
0.4000
0.0810
0.0500
0.0100
0.1100
NR
0.0050
0.0590
0.0190
NR
NR
NR
0.0280
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.5100
NM +-
NM +-
NR +-
NM +-
NR +-
NM +-
NR +-
0.6900 +-
NM +-
9.4000 +-
7.6000 +-
NM +-
0.5900 +-
0.2900 +-
NM +-
NR «•-
1.6000 +-
NR +-
0.5000 +-
NR +-
NR +-
NR +-
0.0130 +-
0.2300 +-
NM +-
NR +-
0.1100 +-
0.0000 +-
NM +-
NM +-
NM +-
0.0100 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM *-
NM +-
NM +-
NM +-
NM +-
0.0500 +-
NR
NR
NR
NR
NR
NR
NR
1.1000
NR
6.7000
5.1000
NR
0.5900
0.3800
NR
NR
0.8300
NR
0.3200
NR
NR
NR
0.0200
0.2100
NR
NR
0.0430
0.0050
NR
NR
NR
0.0100
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0500
0.0000 +-
NM +-
0.6100 +-
NM +-
8.0520 +-
NM +-
0.1952 +-
0.2691 +-
NM +-
14.6460 +-
13.8220 +-
NM +-
0.4192 +-
0.2778 +-
NM +•
4.2273 +-
1.3560 +-
0.0110 +-
0.5000 +-
0.0000 +-
0.0031 +-
0.0000 +-
0.0136 +-
0.1629 +-
NM +-
0.0055 +-
0.1466 +-
0.0177 +-
NM -t-
NM +-
NM +-
0.0198 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.3489 +-
0.1220
NR
0.3050
NR
5.3070
NR
0.1403
1.6490
NR
6.0656
15.9580
NR
0.3582
0.3434
NR
1.5982
0.8727
0.0079
0.4603
0.2440
0.0494
0.0305
0.0139
0.1490
NR
0.0031
0.0528
0.0135
NR
NR
NR
0.0210
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.3306
61 +- 26 % Fine; 41 +-  23 X Coarse fraction
NM = Not Measured;  NR = Not Reported
                            219'
-------
SOURCE: Natural Gas Fired Boiler
Profile: PACS 313
DESCRIPTION: Portland boiler profile measured during PACS.

SPECIES     FINE   +-  UNCERT   COARSE  +-  UNCERT    PM-10  +-  UNCERT
F
CL
N03-
HP04-
S04=
NH4+
NA+
MG+
K+
OC
EC
C03
AL
SI
P
s
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
0.2000 +-
NM +-
2.3000 +-
NM + -
5.2000 +-
NM +-
1.8400 +-
1.0800 +-
NM +-
NM +-
NM +-
NM +-
0.1400 +-
0.1200 +-
NM +-
0.4500 +-
2.3000 +-
0.3300 +-
0.5400 +-
0.0180 +-
0.0460 +-
NR +-
0.0440 +-
0.2100 +-
NM +-
0.0820 +-
0.0220 +-
0.2500 +-
NM +-
NM +-
NM +-
0.0130 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM + -
NM +-
NM + -
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NR +-
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0100 +-
NM +-
0.5000 +-
NM +-
0.5000 H"
NM +-
0.0500 +-
0.0700 +-
NM +-
NM +-
NM +-
NM +-
0.3000 +-
0.3500 +-
NM +-
NR +-
2.2000 +-
1.5000 +-
0.4500 +-
0.1000 +-
0.0180 +-
NR +-
0.0170 +-
0.0430 +-
NM +-
0.0420 +-
0.1170 +-
NR +-
NM +-
NM +-
NM +-
0.0280 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NR +-
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.1620 +-
NM +-
1.9400 +-
NM +-
4.2600 +-
NM +-
1.4820 +-
0.8780 +-
NM +-
NM +-
NM +-
NM +-
0.1720 +-
0.1660 +-
NM +-
0.3600 +-
2.2800 +-
0.5640 +-
0.5220 +-
0.0344 +-
0.0404 +-
0.0000 +-
0.0386 +-
0.1766 +-
NM +-
0.0740 +-
0.0410 +-
0.2000 +-
NM +-
NM +-
NM +-
0.0160 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
80 7, Fine; 20 % Coarse fraction
NM = Not Measured;  NR   Not  Reported


                           220
-------
SOURCE: Rock Crusher                               Profile:  PACS 3111

DESCRIPTION: Portland Rock Crusher profile measured during PACS.

SPECIES    FINE   +•  UNCERT   COARSE  «•-   UNCERT    PM-10  +-   UNCERT
F -
CL -
N03-
HP04-
S04=
NH4+
NA+
MG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
0.0100 +-
NM +-
0.4100 +-
NM +-
0.0500 +-
NM +-
1.9500 +-
1.4300 +-
NM +-
NM +-
NM +-
NM + -
8.0700 +-
29.9400 +-
NM +-
0.0660 +-
0.0100 +-
1.4600 +-
3.3700 +-
0.5600 +-
0.0146 +-
0.0164 +-
0.0810 +-
4.5900 +-
NM +-
0.0039 +-
0.0530 +-
0.0102 +-
NM +-
NM +-
NM +-
0.0038 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM + -
NM +-
NM +-
NM +-
NM +-
NM *-
NM +-
0.0061 +-
0.0100
NR
0.2300
NR
0.0500
NR
0.3200
0.1460
NR
NR
NR
NR
0.3500
0.9700
NR
0.0220
0.0100
0.7400
0.4200
0.0450
0.0022
0.0015
0.0047
0.4700
NR
0.0004
0.0790
0.0033
NR
NR
NR
0.0036
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0065
0.0100 +-
NM +-
0.1000 +-
NM +-
0.0500 +-
NM +-
1.1200 +-
0.8000 +-
NM +-
NM +-
NM +-
NM +•-
7.9900 +-
32.7000 +-
NM +-
0.0610 +-
0.0100 +-
0.9400 +-
2.7200 +-
0.4900 +-
0.0120 +-
0.0110 +-
0.2900 +-
3.7900 +-
NM +-
0.0037 +-
0.0065 +-
0.0061 +-
NM +-
NM +-
NM +-
0.0100 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.0032 +-
0.0100
NR
0.1000
NR
0.0500
NR
0.4500
0.3000
NR
NR
NR
NR
1 .3000
1.4100
NR
0.0021
0.0100
0.1400
0.2700
0.0760
0.0044
0.0031
0.3600
0.4700
NR
0.0016
0.0022
0.0013
NR
NR
NR
0.0100
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0020
0.0105 +-
NM +-
0.2507 +-
NM +-
0.0525 +-
NM +-
1.5661 +-
1.1361 +-
NM +-
NM +-
NM +-
NM +-
8.4271 +-
33.0378 +-
NM +-
0.0664 +-
0.0105 +-
1.2314 +-
3.1615 +-
0.5474 +-
0.0138 +-
0.0141 +-
0.2063 +-
4.3555 +-
NM +-
0.0040 +-
0.0287 +-
0.0083 +-
NM +-
NM +-
NM +-
0.0076 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.0047 +-
0.0105
NR
0.1661
NR
0.0525
NR
0.4114
0.2426
NR
NR
NR
NR
0.9185
1.2737
NR
0.0116
0.0105
0.4290
0.3540
0.0652
0.0036
0.0025
0.2110
0.4935
NR
0.0011
0.0384
0.0023
NR
NR
NR
0.0075
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0042
47 +- 11.2 % Fine;  58.2 *•  5.2 X Coarse fraction
NM = Not Measured;  NR = Not Reported
                               221
-------
SOURCE: Asphalt Batch Plant                        Profile:PACS 3112

DESCRIPTION: Portland Asphalt Batch Plant profile measured during PACS.

SPECIES    FINE   +-  UNCERT   COARSE  +-  UNCERT    PM-10  +-  UNCERT
F
CL -
N03-
HP04-
S04=
NH4+
NA+
MG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
0.0100 +-
NM +-
0.1000 +-
NM +-
0.1000 +-
NM +-
1.4900 +-
1.6800 +-
NM +-
1.9900 + -
0.8400 +-
NM +-
8.6600 +-
27.1300 +-
NM +-
0.2200 +-
0.0100 +-
1.1400 +-
2.8600 +-
0.8600 +-
0.0210 +-
0.0320 +-
0.2000 +-
7.0400 +-
NM +-
0.0069 +-
0.0148 +-
0.0152 +-
NM +-
NM +-
NM +-
0.0080 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.0100 +-
0.0100
NR
0.1000
NR
0.1000
NR
0.0870
0.2100
NR
1.0300
0.4500
NR
0.4500
1.0800
NR
0.1700
0.0100
0.0360
0.2500
0.2600
0.0003
0.0032
0.1400
0.3200
NR
0.0007
0.0011
0.0027
NR
NR
NR
0.0008
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0100
0.0100 +-
NM +-
0.1000 +-
NM +-
0.3700 +-
NM +-
1.8000 +-
1.3300 +-
NM +-
5.0000 +-
1.0400 +-
NM +-
6.3900 +-
24.6500 +-
NM •»•-
NM +-
0.0100 +-
0.5700 +-
2.3200 +-
0.8000 +-
0.0350 +-
0.1150 +-
0.1800 +-
3.9500 +-
NM +-
0.0110 +-
0.1700 +-
0.4200 +-
NM +-
NM +-
NM +-
0.0200 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.0200 +-
0.0100
NR
0.1000
NR
0.5500
NR
1.5200
0.8900
NR
1.0000
0.2100
NR
1.2300
3.5100
NR
NR
0.0100
0.0970
0.3900
0.8400
0.0330
0.0115
0.1600
0.2800
NR
0.0011
0.1100
0.4400
NR
NR
NR
0.0020
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0200
0.0100 +-
NM +-
0.1000 +-
NM +-
0.1189 +-
NM +-
1.5117 +-
1.6555 +-
NM +-
NM +-
NM +-
NM +-
8.5011 +-
26.9564 +-
NM +-
0.2046 +-
0.0100 +-
1.1001 +-
2.8222 +-
0.8558 +-
0.0220 +-
0.0378 +-
0.1986 +-
6.8237 +-
NM +-
0.0072 +-
0.0257 +-
0.0435 +-
NM +-
NM +-
NM +-
0.0088 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.0107 +-
0.0100
NR
0.1000
NR
0.1315
NR
0.1873
0.2576
NR
NR
NR
NR
0.5046
1.2501
NR
0.1581
0.0100
0.0403
0.2598
0.3006
0.0026
0.0038
0.1414
0.3172
NR
0.0007
0.0087
0.0333
NR
NR
NR
0.0009
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0107
93 +- 9 % Fine; 8.4 +-  8.5  % Coarse  fraction
NM = Not Measured;  NR = Not Reported


                             222
-------
SOURCE: Alumina Ore Fugitives                      ProfilerPACS 3173

DESCRIPTION: Portland Alumina Fugitives profile measured during PACS.

SPECIES    FINE   +-  UNCERT   COARSE  +-  UNCERT    PM-10  +-   UNCERT
F
CL
N03-
HP04-
S04=
NH4+
NA+
MG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
0.1200 +-
NM +-
0.5900 *•
NM +-
0.4300 +-
NM +-
0.2400 +-
0.1350 +-
NM +-
NM +-
NM +-
NM +-
36.1000 +-
0.2300 +-
NM +-
0.0610 +-
0.3600 +-
0.0680 +-
0.4800 +-
0.0150 +-
0.0025 +-
0.0165 +-
0.0480 +-
0.3100 +-
NM +-
0.0180 +-
0.0200 +-
0.0120 +-
NM +-
NM +-
NM +-
0.0010 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +•
NM +-
NM «•-
NM +-
0.0500 +-
0.0330
NR
0.2100
NR
0.0990
NR
0.1300
0.0210
NR
NR
NR
NR
6.0000
0.0640
NR
0.0061
0.0420
0.0280
0.1800
0.0057
0.0008
0.0210
0.0120
0.1400
NR
0.0140
0.0020
0.0043
NR
NR
NR
0.0010
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0500
0.0000 +-
NM +-
0.0000 +-
NM +-
1.0000 +-
NM +-
1.5000 +-
0.0000 +-
NM +-
NM +-
NM +-
NM +-
2.2900 +-
0.2100 +-
NM +-
0.0000 +-
0.8500 +-
0.0000 +-
0.2800 +-
0.0130 +-
0.0015 +-
NR +-
0.0540 +-
0.0360 +-
NM +-
NR +-
0.0760 +-
NR +-
NM +-
NM +-
NM +-
0.0200 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NR +-
0.5000
NR
2.0000
NR
0.2500
NR
0.7000
1.0000
NR
NR
NR
NR
1.5800
0.0490
NR
0.0100
0.5000
0.0120
0.1200
0.0110
0.0007
NR
0.0590
0.0440
NR
NR
0.0280
NR
NR
NR
NR
0.0140
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0996 +-
NM +-
0.4897 +-
NM +-
0.5269 +-
NM +-
0.4542 +-
0.1121 +-
NM +-
NM +-
NM +-
NM +-
30.3523 +-
0.2266 +-
NM +-
0.0506 +-
0.4433 +-
0.0564 +-
0.4460 +-
0.0147 +-
0.0023 +-
0.0137 +-
0.0490 +-
0.2634 +-
NM +-
0.0149 +-
0.0295 +-
0.0100 +-
NM +-
NM +-
NM +-
0.0042 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.0415 +-
0.1124
NR
0.5143
NR
0.1247
NR
0.2269
0.1874
NR
NR
NR
NR
5.2486
0.0615
NR
0.0068
0.1199
0.0253
0.1698
0.0066
0.0008
0.0174
0.0200
0.1237
NR
0.0116
.0.0064
0.0036
NR
NR
NR
0.0032
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0415
83 +- 5 % Fine;  17 +-  4 % Coarse fraction
NM = Not Measured; NR  = Not  Reported
                            223
-------
SOURCE: Scrap Metal (Car Shredder) Fugitives        Profile:PACS 3193

DESCRIPTION: Portland Car Shredder Fugitives  profile  from  PACS.

SPECIES    FINE   +-  UNCERT   COARSE  +-   UNCERT     PM-10 +-  UNCERT
F
CL
N03-
HP04-
S04=
NH4+
NA+
MG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
Ni
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
0.0000 +-
NM +-
0.0000 +-
NM +-
0.2900 +-
NM +-
0.1800 +-
0.0000 +-
NM +-
7.7000 + -
0.6000 +-
NM +-
0.4700 +-
0.8700 +-
NM + -
0.4700 + -
0.6800 +-
0.2700 +-
0.4800 +-
0.0000 +-
0.0000 +-
0.0400 +-
0.0880 +-
5.7600 +-
NM +-
0.0310 +-
0.1000 +-
2.1000 +-
NM +-
NM +-
NM +-
0.4900 +-
NM +-
NM +-.
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.4900 +-
0.1000
NR
0.3000
NR
0.0200
NR
0.2400
0.2000
NR
3.3000
0.0600
NR
0.0640
0.1900
NR
0.0850
0.4600
0.1800
0.0570
0.0500
0.0010
0.0007
0.0450
0.9800
NR
0.0070
0.0140
0.1400
NR
NR
NR
0.3500
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0210
NM +-
NM +-
NR +-
NM +-
NR +-
NM +-
NR +-
NR +-
NM +-
31.0000 +-
4.0000 +-
NM +-
1.9000 +-
NR +-
NM +-
NR +-
8.7000 +-
NR +-
5.5000 +-
NR +-
NR +-
NR +-
0.0780 +-
3.7000 +-
NM +-
NR +-
0.9900 +-
0.8700 +-
NM +-
NM +-
NM +-
8.4000 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.0500 +-
NR
NR
NR
NR
NR
NR
NR
NR
NR
2.8000
4.2000
NR
0.3500
NR
NR
NR
0.7900
NR
0.7100
NR
NR
NR
0.1000
1.1000
NR
NR
0.3000
0.1200
NR
NR
NR
1.1000
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0500
0.0000 +-
NM +-
0.0000 +-
NM +-
0.2900 +-
NM +-
0.1800 +-
0.0000 +-
NM +-
7.7000 +-
0.6000 +-
NM +-
0.4700 +-
0.8700 +-
NM +-
0.4700 +-
0.6800 +-
0.2700 +-
0.4800 +-
0.0000 +-
0.0000 +-
0.0400 +-
0.0880 +-
5.7600 +-
NM +-
0.0310 +-
0.1000 +-
2.1000 +-
NM +-
NM +-
NM +-
0.4900 +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
NM +-
0.4900 +-
0.1000
NR
0.3000
NR
0.0200
NR
0.2400
0.2000
NR
3.3000
0.0600
NR
0.0640
0.1900
NR
0.0850
0.4600
0.1800
0.0570
0.0500
0.0010
0.0007
0.0450
0.9800
NR
0.0070
0.0140
0.1400
NR
NR
NR
0.3500
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.0210
94 +- 1 % Fine;  6 +-  1  % Coarse  fraction
NM   Not Measured;  NR  = Not  Reported


                              224
-------
Pacific Northwest Source Profile Project
LOCATION:Eugene,  OR

SOURCE:  Ueyerhauser Recovery Furnace
Profile: 23104
DESCRIPTION:       Fine is average of:  DTS155/DQS155,  DTS157/DQS157,  and
DTS/DQS159.  Coarse is average of: DTS156/DQS156, DTS158/DOS158.  and
DTS160/DQS160.
SPECIES     FINE   +-    UNCERT    COARSE   +-   UNCERT    PM-10    +-   UNCERT
F -
CL -
N03-
HP04-
S04=
NH4+
NA+
MG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
HN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
0.000000 +-
3.058800 +-
0.351000 +-
0.000000 +-
54.844800 +-
1.060667 +-
25.832300 +-
0.018400 +-
2.490733 +-
5.233367 +-
1.530067 +-
0.010333 +•
0.092333 +-
0.303300 +-
0.000000 +-
12.977200 +-
3.058800 +-
2.490733 +-
0.620867 +-
0.004200 +-
0.003200 +-
0.003167 +-
0.002767 +-
0.067033 +-
0.001267 +-
0.000600 +-
0.005800 +-
0.014233 +-
0.000000 +-
0.000633 +-
0.000000'+-
0.072167 +-
0.006467 +-
0.003300 +-
0.000600 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.003567 +-
0.000000 +-
0.000000 +-
0.001500 + •
0.000000 +-
0.000000 +-
0.000800 +-
0.000000 +-
0.048464
0.411585
0.063704
0.130730
15.821370
0.828752
7.790816
0.026022
0.362314
2.428806
1.185522
0.044934
0.130579
0.162140
0.432088
2.597360
0.406338
0.362314
0.387315
0.045847
0.018969
0.004994
0.003353
0.034289
0.002315
0.001782
0.006969
0.009165
0.007204
0.005402
0.002902
0.047153
0.001618
0.002540
0.004150
0.005359
0.009429
0.017644
0.020887
0.022970
0.026917
0.036513
0.040224
0.144875
0.162762
0.010403
0.009046
0.000000 +-
6.760267 +-
0.795233 +-
0.000000 +-
38.162633 +-
1.145267 +-
29.314300 +-
0.049267 +-
2.462333 +-
18.440967 +-
8.281600 +-
0.215600 +-
0.313100 +-
0.009267 +-
0.000000 +-
12.494567 +-
2.976033 +-
2.462333 +-
0.000000 +-
0.003333 +-
0.008933 +-
0.000000 +-
0.004233 +-
0.016367 +-
0.001500 +-
0.000000 +-
0.001667 +-
0.001867 +-
0.003367 +-
0.002100 +-
0.000300 +-
0.009433 +-
0.001933 +-
0.001200 +-
0.002567 +-
0.000000 +-
0.011900 +-
0.000000 +-
0.000367 +-
0.003367 +•
0.000000 +-
0.016700 +-
0.025500 +-
0.065900 +-
0.000000 +•
0.003733 +-
0.000833 +-
0.372691
7.355533
0.463202
1.005525
12.806683
1.067551
14.137521
0.134780
0.630056
15.439686
9.143360
0.349680
1.123697
0.460534
2.067237
5.658048
0.479908
0.383176
0.109993
0.344772
0.142583
0.036619
0.026047
0.016570
0.016115
0.013040
0.010957
0.015159
0.054107
0.039510
0.021540
0.013341
0.016315
0.019951
0.030218
0.039469
0.069788
0.131193
0.156354
0.171136
0.201755
0.274567
0.301832
1.091712
1.226630
0.076571
0.066818
0.000000 +-
4.625533 +-
0.420333 +-
0.000000 +-
51.036300 +-
1.071800 +-
25.968300 +-
0.024100 +-
2.484233 +-
7.168667 +-
2.636567 +-
0.036767 +-
0.121833 +-
0.253700 +-
0.000000 +-
12.931933 +-
3.039900 +-
2.484233 +-
0.516433 +-
0.004167 +-
0.004033 +-
0.002700 +-
0.003133 +-
0.058800 +-
0.001367 •»•-
0.000500 +-
0.005267 +-
0.012300 +-
0.000567 +-
0.000933 +-
0.000033 +•
0.060967 +-
0.005667 +-
0.002967 +-
0.000867 +-
0.000000 +-
0.001867 +-
0.000000 +-
0.000067 +-
0.003400 +-
0.000000 +-
0.002333 +-
0.006233 +-
0.013967 +-
0.000000 *-
0.001267 +-
0.000167 +-
0.069884
2.659251
0.088022
0.188518
11.513205
0.876102
3.773371
0.034083
0.353433
3.813594
1.707939
0.064893
0.175410
0.147245
0.502098
3.213574
0.417519
0.353433
0.341021
0.065301
0.026979
0.006960
0.004862
0.031564
0.003091
0.002513
0.006219
0.007874
0.010250
0.007589
0.004097
0.036956
0.002891
0.003909
0.005835
0.007564
0.013342
0.025033
0.029666
0.032553
0.038285
0.051975
0.057262
0.206702
0.232129
0.014669
0.012791
                              225
-------
SOURCE: Ueyerhauser Recovery Furnace
SPECIES FINE +- UNCERT COARSE +- UNCERT PM-10 +-
FLOR
OIBE
PHEN
ANTH
ACRI
CARS
FLUO
PYRE
RETE
BEMB
BECP
CHRY
BE8F
BEEP
BAP
PERY
INDE
DIAA
BEGP
TETR
PENT
HEXA
HEPT
OCTA
NONA
TRIA
0.000044 +-
0.000124 +-
0.000505 +-
0.000500 +-
0.000402 +-
0.000079 + -
0.000315 +-
0.000465 +-
0.002387 +-
0.000407 +-
0.000079 +-
0.000285 +-
0.000079 +-
0.000084 +-
0.000079 +-
0.000079 +-
0.000079 + -
0.000079 «•-
0.000079 +-
0.003450 +-
0.005300 +•
0.002500 +-
0.002700 +-
0.001650 +-
0.001250 +-
0.001137 +-
0.000015 +-
0.000077 +-
0.000168 +-
0.000178 +-
0.000318 +-
0.000080 +-
0.000123 *-
0.000185 +-
0.002313 +-
0.000333 *-
0.000080 +-
0.000095 +-
0.000080 +-
0.000057 *-
0.000080 +-
0.000080 +-
0.000080 +-
0.000080 +-
0.000080 +-
0.001165 +-
0.001811 +•
0.000871 +-
0.000911 +-
0.000650 +-
0.000423 +-
0.001063 +-
0.000044 +-
0.000124 *-
0.000505 +-
C. 000500 +-
0.000402 +-
0.000079 +-
0.000315 +-
0.000465 *-
0.002387 +-
0.000407 +-
0.000079 +-
0.000285 +-
0.000079 +-
0.000084 «•-
0.000079 +-
0.000079 +-
0.000079 +-
0.000079 +-
0.000079 +-
0.003450 +-
0.005300 +-
0.002500 +-
0.002700 +-
0.001650 +-
0.001250 +-
0.001137 +-
UNCERT
0.000015
0.000077
0.000168
0.000178
0.000318
0.000080
0.000123
0.000185
0.002313
0.000333
0.000080
0.000095
0.000080
0.000057
0.000080
0.000080
0.000080
0.000080
0.000080
0.001165
0.001811
0.000871
0.000911
0.000650
0.000423
0.001063
PM-10 fraction assumed to have same composition as fine fraction.
                             226
-------
13-Jun-85
                                                  SOURCE LIBRARY

SPECIES
NUMBER
4
5
9
11
13
14
15
16
17
19
20
22
23
24
25
26
28
29
30
33
34
35
37
38
39
40
42
46
47
48
50
51
56
57
58
80
82
201
202
203
204
SUM< % >
NOTES:
SOURCE:
SCC:
CONTROLS:
SPECIES
NAME
BE
B
F
NA
AL
SI
P
s
CL
K
CA
TI
V
CR
MN
FE
NI
CU
ZN
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
SN
SB
BA
LA
CE
HG
PB
OC
EC
S04
N03

LIME KILN
3-07-001-06
UET SCRUBBER
*********
X BY UT
NA
NA
0.038
36.210
0.064
0.038
0.105
16.520
2.618
1.299
0.342
0.004
0.068
0.011
0.015
0.041
0.032
0.005
0.006
0.003
0.003
0.024
0.006
0.003
0.003
0.012
0.004
0.006
0.027
0.015
0.047
0.019
0.029
0.099
0.118
0.002
0.018
9.280
0.464
48.830
0.092
100.000
OC = ORGANIC CARBON
FINE
<2.5 UM ******
+ • UNC
f • NR
+ • NR
+ - 0.007
+ • 4.000
+ - 0.074
+ - 0.042
* • 0.227
+ - 1.780
+ • 0.282
+ - 0.140
+ • 0.037
+ - 0.003
+ - 0.007
+ • 0.003
+ - 0.003
+ • 0.009
+ • 0.005
+ - 0.004
+ • 0.002
+ - 0.007
+ • 0.002
+ - 0.004
+ - 0.004
+ • 0.005
+ • 0.003
+ • 0.012
t- • 0.009
* • 0.006
+ • 0.020
+ - 0.015
+ • 0.032
* • 0.019
+ • 0.029
+ • 0.107
* - 0.127
+ - 0.004
+ - 0.011
+ • 1.000
+ - 0.500
1- - 8.000
+ - 0.100

: EC = ELEMENTAL
*********
% BY UT
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.000
CARBON : NA =
COARSE
2.5-10UM ******
+- UNC
+ • NR
* - NR
+ - NR
+ - NR
+ - NR
+ • NR
+ - NR
+ • NR
+ • NR
+ - NR
+ • NR
+ • NR
+ - NR
+ - NR
+ • NR
+ - NR
+ • NR
+ • NR
+ - NR
+ - NR
+ • NR
+ - NR
+ - NR
«• • NR
+ - NR
+ • NR
+ • NR
+ • NR
+ - NR
+ - NR
+ - NR
+ - NR
+ • NR
+ - NR
+ - NR
+ • NR
+ • NR
+ - NR
«• - NR
* - NR
+ - NR

NOT ANALYZED : NR
PROFILE: 23202
RANKING: 3324
RATING : B
TSP
********* <30 UM
% BY UT +•
NA + •
NA •»• -
1.296 + •
34.680 + •
0.303 + -
0.200 + -
0.175 + -
16.040 + -
2.630 + •
1.280 + -
0.390 * -
0.004 * -
0.063 + -
0.015 * -
0.022 + •
0.066 + -
0.047 * •
0.006 * -
0.013 + -
0.005 * -
0.005 + •
0.023 * -
0.011 + -
0.009 + -
0.005 + -
0.020 + -
0.033 + •
0.015 + -
0.068 * •
0.026 + -
0.069 + •
0.032 + -
0.049 + -
0.169 + -
0.201 + •
0.004 * •
0.023 + •
10.120 + •
0.576 + -
47.197 + -
0.150 + -
100.000
= NOT REPORTED
******
UNC
.NR
NR
0.240
3.681
0.094
0.056
0.195
1.703
0.326
0.136
0.042
0.003
0.007
0.004
0.004
0.012
0.006
0.004
0.003
0.007
0.003
0.004
0.005
0.006
0.003
0.014
0.019
0.012
0.025
0.018
0.038
0.023
0.035
0.127
0.151
0.005
0.013
1.724
0.481
6.881
0.113


            < = LESS THAN DETECTION LIMIT
            OTHER NOTES :      DATA NORMALIZED TO  100% WITH A 6X CORRECTION FACTOR.REF.  49.
                                                   227
-------
Pacific Northwest Source Profile Project
LOCATION:  Eugene OR
SOURCE:  University of Oregon Hogged Fuel  Boiler
Profile: 12706
DESCRIPTION:       Fine data are the average of DTS001/DQS041,
DTS005/DQS045, AND DTS007/DOS047.   Coarse data are the average  of
DTS002/DQS042 and DTS008/DQS048.
SPECIES     FINE   +-   UMCERT    COARSE  +-   UNCERT     PM-10   +-
               UNCERT
F
CL -
N03-
HP04-
S04=
NH4+
NA+
HG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
HO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB

0.000000 +-
2.538767 +-
0.135333 +-
1.056767 +-
26.355267 +-
0.017833 +-
1 .447967 +-
0.050867 +-
24.208367 +-
2.482767 +-
1.069367 +-
0.183367 +-
0.000000 +-
0.150533 +-
0.000000 +-
8.994500 +-
3.702900 +-
22.608733 +-
0.440767 +-
0.018867 +-
0.008700 +-
0.025000 +-
0.198900 +-
0.667633 +-
0.001967 +-
0.003767 +-
0.140967 +-
1.490000 +-
0.000000 +-
0.049367 +-
0.003000 +-
0.087367 +-
0.077667 +-
0.009067 +-
0.002067 +•
0.001533 +-
0.020067 +-
0.000800 +-
0.000500 +-
0.000633 +-
0.000200 +-
0.016133 +-
0.005400 +-
0.029333 +-
0.000000 +-
0.000900 +•
0.135233 +-

0.027223
0.190146
0.045213
0.259079
4.394277
0.016370
0.107523
0.010472
4.149752
3.105409
0.666264
0.149096
0.098166
0.112089
0.319692
3.923554
0.529059
6.971770
0.268270
0.025839
0.010828
0.006982
0.035706
0.103339
0.009048
0.000547
0.015853
0.112277
0.005137
0.007493
0.001208
0.006792
0.005666
0.003472
0.003982
0.002890
0.003943
0.009942
0.011672
0.012852
0.015364
0.010134
0.021902
0.078387
0.088952
0.005637
0.015893
22
0.000000 +-
0.804100 +-
0.116450 +-
1.926200 +-
11.302050 +-
0.000000 +-
0.550500 +-
0.704300 +-
9.326750 +-
10.507100 +-
4.402700 +-
0.487100 +-
4.029400 +-
3.867500 +-
. 1.261550 +-
8.725350 +-
1.499850 +-
13.872850 +-
13.953250 +-
0.146250 +-
0.015350 +-
0.018750 +-
0.704600 +-
2.649600 +-
0.004350 +-
0.004900 +-
0.068350 +-
0.480750 +-
0.000250 +-
0.019150 +-
0.003050 +-
0.021150 +-
0.026350 +-
0.132300 +-
0.001400 +-
0.003200 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.006850 +-
0.000000 +-
0.000500 +-
0.003050 +-
0.303050 +-
0.005900 +-
0.006500 +-
0.039050 +-
8
0.112271
0.256351
0.136082
0.336613
0.876144
0.067402
0.134446
0.066603
0.706126
3.666729
2.750695
0.110958
1.379888
1 .323331
1.687158
3.085293
0.474944
2.932814
2.695422
0.080590
0.047507
0.006055
0.054135
0.200284
0.048902
0.001803
0.007003
0.037900
0.019076
0.019476
0.004302
0.004441
0.005179
0.010806
0.013671
0.013450
0.016530
0.041189
0.048487
0.053379
0.062881
0.063781
0.092940
0.301868
0.369179
0.023661
0.012210

0.000000 +-
2.205500 +-
0.120533 +-
1.165900 +-
23.009400 +-
0.013533 +-
1.294433 +-
0.172400 +-
22.272767 +-
3.458267 +-
1.652267 +-
0.256233 +-
0.768600 +-
0.873300 +-
0.243500 +-
8.386500 +-
3.204133 +-
19.924233 +-
3.059033 +-
0.040300 +-
0.009100 +-
0.023000 +-
0.292900 +-
1.037433 +-
0.002500 +-
0.003967 +-
0.125900 +-
1.292933 +-
0.000067 +-
0.043333 +-
0.002933 +-
0.075900 +-
0.068000 +-
0.033100 +-
0.001900 +-
0.001833 +-
0.015833 +-
0.000800 +-
0.000500 +-
0.002167 +-
0.000133 *-
0.013267 +-
0.005900 +-
0.088233 +-
0.000833 +-
0.001967 +-
0.116367 +-

0.032093
0.313904
0.039467
0.315834
2.886183
0.019255
0.216127
0.100469
5.349521
2.656905
0.786294
0.072746
0.630023
0.757811
0.452682
2.870625
0.225059
3.703046
2.526636
0.029137
0.013518
0.004825
0.107148
0.390319
0.013579
0.000547
0.008083
0.116177
0.005771
0.007241
0.001115
0.015166
0.006388
0.024350
0.004251
0.003758
0.004282
0.011738
0.013857
0.015251
0.018047
0.013585
0.026107
0.084264
0.105397
0.006717
0.011483

-------
Pacific Northwest Source Profile Project
SOURCE:  University of Oregon Hogged Fuel Boiler
SPECIES     FINE   + •   UNCERT    COARSE  *-   UNCERT
PH-10
UNCERT
FLOR
DIBE
PHEN
ANTH
ACRI
CARB
TLUO
PYRE
RETE
BENB
BECP
CHRY
BEBF
BEEP
BAP
PERY
INOE
DIAA
.BEGP
TETR
PENT
HEXA
HEPT
OCTA
NONA
TRIA
0.0000*3 *•
0.000043 + •
0.000353 +-
0.000328 +-
0.000053 +-
0.000053 *•
0.000224 f-
0.000648 +-
0.003962 +-
0.000482 +•
0.000053 +-
0.000242 +-
0.000025 +-
0.000096 +-
0.000054 +-
0.000053 +-
0.000048 +-
0.000053 *•
0.000053 +-
0.001770 +-
0.002646 +-
0.002085 *-
0.001502 +-
0.000960 *-
0.000516 +-
0.000644 +-
0.000030 +-
0.000018 *-
0.000168 *-
0.000194 +-
0.000062 +•
0.000062 +-
0.000114 +-
0.000282 +-
0.003107 +-
0.000266 +-
0.000062 +-
0.000188 +•
0.000025 +•
0.000082 +-
0.000058 +-
0.000062 +•
0.000061 +-
0.000062 +-
0.000062 +-
0.001512 +-
0.002599 +•
0.002232 +•
0.001500 +-
0.000768 *-
0.000470 +-
0.000674 +-
0.000043 +-
0.000043 *-
0.000353 +-
0.000328 +-
0.000053 +•
0.000053 +-
0.000224 *-
0.000648 +-
0.003962 +-
0.000482 +-
0.000053 +-
0.000242 +-
0.000025 +-
0.000096 +-
0.000054 +-
0.000053 +-
0.000048 +-
0.000053 +-
0.000053 *-
0.001770 +-
0.002646 *-
0.002085 +•
0.001502 +-
0.000960 +-
0.000516 +-
0.000644 +-
0.000030
0.000018
0.000168
0.000194
0.000062
0.000062
0.000114
0.000282
0.003107
0.000266
0.000062
0.000188
0.000025
0.000082
0.000058
0.000062
0.000061
0.000062
0.000062
0.001512
0.002599
0.002232
0.001500
0.000768
0.000470
0.000674
PH-10 fraction assumed to have same composition as fine  fraction.
                              -229
-------
13-Jun-85
                                                 SOURCE LIBRARY


SPECIES
NUMBER
4
5
9
11
12
13
14
15
16
17
19
20
22
23
25
26
27
28
29
30
31
33
34
35
37
38
40
42
46
47
43
49
50
51
56
57
80
82
83
200
201
202
203
204
SUM( % )
SOURCE:
SCC:
CONTROLS:

SPECIES
NAME
BE
B
F
NA
MG
AL
SI
P
S
CL
K
CA
TI
V
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
BI
TC
OC
EC
S04
N03

ALUMINUM 1
3-03-001'
NONE

X BY WT
<
0.190
13.500
14.900
0.055
15.200
0.340
0.030
5.000
0.800
0.527
0.100
0.002
0.015
0.008
0.114
0.002
0.014
0.018
0.007
0.028
0.022
0.003
0.022
0.005
<
<
0.006
<
<
0.003
<
<
0.001
0.001
0.004
<
0.072
0.030
NA
28.200
2.680
17.411
0.690
100.000
(EDUCTION POTLINE
•07
FINE
<2.5 UM ******
+ • UNC
+ - NR
+ • 0.020
+ • 5.900
+ • 1.700
+ • 0.006
+ - 1.700
+ - 0.040
+ • 0.030
+ - 3.800
+ - 0.160
+ - 0.470
+ • 0.140
+ - NR
+ - 0.004
+ • 0.011
* - 0.095
+ • 0.002
* - 0.008
+ - 0.008
+ • 0.001
* - 0.018
+ - 0.014
+ • NR
+ - 0.008
+ • 0.001
+ • NR
* - NR
+ • 0.006
+ - NR
+ - NR
+ - 0.001
+ • NR
+ - NR
+ - 0.003
» - NR
+ • 0.004
+ • NR
+ - 0.026
* - 0.030
+ • NR
5.000
+ 0.320
+ - 9.300
+ 0.130



*********
X BY WT
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.000

COARSE
2.5-10UM ******
+ - UNC
+ - NR
+ • Ntf
+ • NR
+ • NR
+ - NR
+ - NR
+ - NR
+ - NR
+ NR
+ • NR
+ - NR
+ NR
+ • NR
+ • NR
+ NR
+ - NR
+ • NR
+ - NR
+ - NR
* - NR
+ • NR
+ - NR
+ • NR
+ • NR
+ • NR
+ - NR
+ • NR
+ • NR
+ • NR
* - NR
+ • NR
+ • NR
+ • NR
+ - NR
+ • NR
+ - NR
+ • NR
+ • NR
+ • NR
+ • NR
+ • NR
+ • NR
+ • NR
+ - NR

PROFILE:
RANKING:
RATING :

*********
X BY WT
NA
NA
15.454
NA
NA
15.926
0.398
0.042
3.908
0.834
0.358
0.414
0.015
0.073
0.004
0.812
NA
0.288
0.078
0.006
0.050
0.018
0.002
0.016
0.004
0.003
<
0.012
<
<
0.002
<
<
0.001
0.002
0.004
<•
0.053
NA
NA
22.180
15.247
12.764
0.593
89.561
29102
3324
B
TSP
<30 UM ******
+• UNC
+ - NR
+ • NR
+ - 3.387
+ • NR
+ • NR
+ - 1.657
+ • 0.047
+ - 0.019
+ - 2.065
+ - 0.338
* - 0.254
+ • 0.083
* - 0.002
+ - 0.013
+ 0.006
+ - 0.281
+ - NR
+ - 0.078
+ • 0.011
+ - 0.003
+ • 0.014
+ • 0.008
+ • NR
+ - 0.004
•»• • NR
+ - NR
+ - NR
+ - 0.005
+ • NR
* - NR
+ - 0.001
•»• - NR
+ - NR
+ - 0.002
+ - 0.001
+ • 0.003
+ • NR
+ • 0.014
+ ' NR
* - NR
+ - 3.032
+ 2.765
+ - 5.043
+ - 0.086

  NOTES:   OC = ORGANIC CARBON  :   EC = ELEMENTAL CARBON :  NA = NOT ANALYZED
           < = LESS THAN DETECTION LIMIT
           OTHER NOTES : REF. 49.  FINE FRACTION CORRECTED BY 8% TO NORMALIZE TO 100X
NR = NOT REPORTED
                                                 230
-------
Pacific Northwest Source Profile Project







LOCATION:   Medford.OR





SOURCE:   Wood Sander Dust (MedCo)




DESCRIPTI  Raw wood dust (NEA49)
                                       Profile: 22203
SPECIES
FINE   -i-  UNCERT   COARSE  +-  UNCERT    PM-10   +-   UMCERT
F- +-
CL- +-
N03- +-
HP04- +-
S04= +-
NH4+ +-
NA+ +-
MG+ +-
K+ +-
OC +-
EC +-
C03 +-
AL +•
SI +•
P +-
S +-
CL +-
K +-
CA +-
TI +-
V +-
CR +-
HN +•
FE f-
CO +-
HI +•
CD +-
ZN +-
GA +-
AS +-
SE +-
BR +- '
RB +-
SR *-
Y +-
ZR +-
MO *•
PD +-
AG +-
CD +•
IN +-
SN *-
SB *'
BA +-
LA *-
HG +-
PB +-
+- 0.000000 +-
+- 0.033700 +-
+- 0.000000 +-
+- 0.000000 +-
+- 0.000000 +-
+- 0.163400 +-
+- 0.231500 *-
+- 0.078800 +-
+- 0.107500 +-
+- 36.511900 +-
+- 4.490500 +-
+- 0.000000 *-
+- 0.552500 +-
+- 2.922800 +-
+- 0,016500 +-
+- 0.038500 +-
*- 0.016900 +-
+- 0.188400 +-
+- 0.511700 *-
+- 0.010000 +-
+- 0.000000 +-
*- 0.002600 +-
+- 0.017000 +-
+- 0.312800 +-
+- 0.001700 +-
+- 0.000500 +-
+- 0.018000 +-
+- 0.008400 +-
+- 0.000000 +-
+• 0.000000 +-
+- 0.000700 +-
+- 0.000000 +-
+- 0.001800 +-
*- 0.001500 +-
+- 0.000000 +-
+- 0.000000 +-
+- 0.000000 «•-
+• 0.000000 +-
+- 0.000000 +-
+- 0.000000 +-
+- 0.003400 *•
+• 0.000000 +-
+- 0.016300 +-
*- 0.080400 +-
+- 0.110400 +-
+- 0.000000 +-
+• 0.000000 +-
0.105800
0.070900
0.031100
0.263300
0.064900
0.122900
0.026300
0.012100
0.025500
4.604700
1 .662700
0.171700
0.178000
0.939200
0.026500
0.006100
0.043200
0.016400
0.091200
0.074500
0.030700
0.007400
0.002500
0.023400
0.005900
0.002700
0.002000
0.001600
0.009200
0.008500
0.004600
0.003800
0.004500
0.005400
0.006300
0.008300
0.014200
0.026400
0.032100
0.034500
0.041500
0.055200
0.064100
0.226400
0.259600
0.016100
0.013100
                               231
-------
Pacific Northwest Source Profile  Project
LOCATION:  Medford,  OR

SOURCE:  Boise Cascade Veneer  Driers
Profile: 22302
DESCRIPTION:        Five steam heated Douglas  fir veneer driers
operating at  375 degrees f,  with wet scrubber controls.
SPECIES
            FINE
                        UNCERT   COARSE  +-  UNCERT
                                                      PM-10
                                                                   UNCERT
F-
CL-
N03-
HP04-
S04=
NH4+
NA+
HG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
0.000000 +-
0.005067 +-
0.037100 +-
0.057167 +-
0.017800 +-
0.000000 +-
0.008667 +-
0.002900 + -
0.003533 +-
69.760767 +-
1.832333 +-
0.007567 +-
0.000000 +-
0.015533 +-
0.000000 +-
0.028700 +-
0.017467 +-
0.003200 +-
0.005800 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.001033 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 + -
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000167 +-
0.002967 +-
0.010467 +-
0.000000 +-
0.000000 +-
0.004309 +-
0.009592 +-
0.013471 +-
0.020452 +-
0.007669 +-
0.002593 +-
0.004978 +-
0.001548 +-
0.001702 +-
10.448911 +-
0.405293 +-
0.009389 +-
0.004661 +-
0.003981 +-
0.001619 +-
0.012738 +-
0.006876 +-
0.000572 +-
0.000701 +-
0.004642 +-
0.001941 +-
0.000504 +-
0.000368 «•-
0.000826 +-
0.000199 +-
0.000199 +-
0.000269 +-
0.000298 +-
0.000769 +-
0.000602 +-
0.000335 +-
0.000269 +-
0.000335 +-
0.000368 +-
0.000434 +-
0.000602 +-
0.001065 +-
0.001804 +-
0.002100 +-
0.002276 +-
0.002741 +-
0.003646 +-
0.004080 +-
0.014514 +-
0.016449 +-
0.001134 +-
0.000966 +-
0.000000 +-
0.005067 +-
0.037100 +-
0.057167 +-
0.017800 +-
0.000000 +-
0.008667 +-
0.002900 +-
0.003533 +-
69.760767 +-
1.832333 +-
0.007567 +-
0.000000 +-
0.015533 +-
0.000000 +-
0.028700 +-
0.017467 +-
0.003200 +-
0.005800 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.001033 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +•
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000000 +-
0.000167 +-
0.002967 +-
0.010467 •»•-
0.000000 +-
0.000000 +-
0.004309
0.009592
0.013471
0.020452
0.007669
0.002593
0.004978
0.001548
0.001702
10.448911
0.405293
0.009389
0.004661
0.003981
0.001619
0.012738
0.006876
0.000572
0.000701
0.004642
0.001941
0.000504
0.000368
0.000826
0.000199
0.000199
0.000269
0.000298
0.000769
0.000602
0.000335
0.000269
0.000335
0.000368
0.000434
0.000602
0.001065
0.001804
0.002100
0.002276
0.002741
0.003646
0.004080
0.014514
0.016449
0.001134
0.000966
                          232
-------
Pacific Northwest Source Profile Project
SOURCE:  Boise Cascade Veneer Driers
SPECIES     FINE   «•-   UNCERT   COARSE
+-  UNCERT    PM-10
UNCERT
FLOR
DIBE
PHEN
ANTH
ACRI
CARB
FLAN
PYRE
RETE
BENB
BECP
CHRY
BEBF
BEEP
BAP
PERY
INDE
DIAA
BEGP
TETR
PENT
HEXA
KEPT
OCTA
NONA
TRIA
0.000031 +-
0.000056 +-
0.001022 +-
0.001042 +•
0.000152 +-
0.000152 +-
0.000152 +-
0.001177 +-
0.031075 +-
0.000152 +-
0.000152 +-
0.000448 +-
0.000224 +-
0.000549 +-
0.000602 +•
0.000237 +•
0.000164 +-
0.000152 +-
0.000406 +-
0.000152 +-
0. 007574 .+-
0.000542 +•
0.002572 +-
0.000152 +-
0.000814 +-
0.000152 +-
0.000016 +-
0.000019 +-
0.000339 +-
0.000870 +-
0.000153 +-
0.000153 +-
0.000153 +-
0.000472 +-
0.030943 •*•-
0.000153 +-
0.000153 +-
0.000334 +-
0.000128 +-
0.000416 *-
0.000390 +-
0.000123 +-
0.000128 +-
0.000153 +-
0.000273 +-
0.000153 +-
0.005075 +-
0.000409 +-
0.002440 +-
0.000153 +-
0.000487 +-
0.000153 +•
0.000031 «•-
0.000056 +-
0.001022 +-
0.001042 +-
0.000152 +-
0.000152 +-
0.000152 +-
0.001177 +-
0.031075 +-
0.000152 +-
0.000152 «•-
0.000448 +-
0.000224 +-
0.000549 +-
0.000602 +-
0.000237 +-
0.000164 +-
0.000152 +-
0.000406 +-
0.000152 +-
0.007574 +-
0.000542 +-
0.002572 +-
0.000152 +-
0.000814 +-
0.000152 +-
0.000016
0.000019
0.000339
0.000870
0.000153
0.000153
0.000153
0.000472
0.030943
0.000153
0.000153
0.000334
O.OC0128
0.000416
0.000390
0.000123
0.000128
0.000153
0.000273
0.000153
0.005075
0.000409
0.002440
0.000153
0.000487
0.000153
                            233
-------
Pacific Northwest Source Profile Project
LOCATION:  Hedford,  OR

SOURCE:  Medco Hogged Fuel  Boiler
Profile: 12707
DESCRIPTION:       Fine data are  the  average  of DTS041/DOS001,
DTS04F3/DQS003,  and DTS045/DQS005.  Coarse data are  the  average  of
DTS042/DQS002,  DTS044/DQS004,  and DTS046/DQS006.
SPECIES     FINE   +-    UNCERT   COARSE  +-   UNCERT     PM-10    +-    UNCERT
F-
CL-
N03-
HP04-
S04=
NH4+
NA+
MG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
HO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
0.000000 +-
3.284733 +-
0.624433 +-
0.454733 -I'-
ll. 176567 + -
0.000000 +-
16.437100 +-
0.671933 +-
17.275200 +-
7.180733 +-
0.267200 +-
5.101567 +-
0.126400 +-
0.146033 +-
0.000000 +-
5.126033 +-
3.357933 +-
18.053900 +-
3.322000 +-
0.009933 «•-
0.006267 +-
0.007233 +-
0.695867 +-
0.407833 +•
0.001533 +-
0.002067 +-
0.025733 +-
0.192833 +-
0.000233 +-
0.003933 +-
0.002600 +-
0.015833 +-
0.023400 +-
0.091833 +-
0.000767 +-
0.001100 +-
0.001600 +-
0.001933 +-
0.000000 +-
0.001167 + -
0.000000 +-
0.000000 +-
0.000000 +-
0.189133 +-
0.000000 +-
0.001300 +-
0.140800 +-
0.014961
1.212273
0.351492
0.163050
7.094315
0.009092
2.352067
0.301758
2.047570
3.006824
0.365561
1.577282
0.090500
0.033759
0.167373
0.363292
1.153964
1.509886
0.508107
0.022884
0.009453
0.001135
0.110942
0.029390
0.005484
0.000238
0.001904
0.015080
0.002700
0.022311
0.001417
0.002380
0.001735
0.018433
0.002043
0.003918
0.002863
0.005798
0.006623
0.007288
0.008522
0.011466
0.012432
0.024782
0.049383
0.003231
0.074292
0.000000 +-
1.548700 +-
0.560267 +-
0.956367 +-
20.127767 +-
0.000000 +-
3.333067 +-
0.624367 +-
7.689067 +-
7.180733 +-
3.510567 •*•-
0.345133 +-
0.708633 +-
0.554267 +-
0.001600 +-
4.221433 +-
1.898533 +-
9.786300 +-
3.936567 +-
0.017867 +-
0.005667 +-
0.000000 +-
0.324233 +-
0.199800 +-
0.001000 +-
0.000000 +-
0.007133 +-
0.063333 +-
0.000000 +-
0.004967 +-
0.000000 +-
0.005267 +-
0.006033 +-
0.042433 +-
0.000233 +-
0.000000 +-
0.000000 +-
0.005833 +-
0.010267 +-
0.001433 +-
0.000000 +-
0.013967 +-
0.022233 +-
0.140567 +-
0.076500 +-
0.001100 +-
0.018633 +-
0.162996
0.692214
0.202730
0.446866
10.783830
0.097929
0.995830
0.190620
4.098494
3.006824
3.976357
4.191609
1.130481
0.734880
2.835962
1.519077
0.621496
3.351462
1.442516
0.260608
0.107407
0.016461
0.116274
0.061857
0.065833
0.004770
0.006593
0.038417
0.032608
0.303563
0.007965
0.006856
0.005747
0.009864
0.025076
0.045945
0.032254
0.064717
0.075170
0.081594
0.095730
0.128528
0.141115
0.302087
0.558205
0.037356
0.021652
0.000000 +-
3.162100 +-
0.586433 +-
0.485500 +-
11.342667 +-
0.000000 +-
14.819767 «•-
0.635400 +-
16.564000 +-
7.180733 +-
0.693033 +-
4.468500 +•
0.156233 +-
0.182233 +-
0.000100 ••-
5.024567 +-
3.227600 +-
17.223067 +-
3.335467 +-
0.010267 +-
0.006133 +-
0.006400 +-
0.655167 +-
0.386267 +-
0.001467 +-
0.001867 +-
0.024033 +-
0.180200 +-
0.000200 +-
0.004200 +-
0.002400 +-
0.014867 +-
0.021800 +-
0.086700 +-
0.000700 +-
0.000933 +-
0.001367 +-
0.002000 +-
0.000733 +-
0.001400 +-
0.000000 +-
0.000800 +-
0.001300 +-
0.181567 +-
0.006300 +-
0.001333 •»•-
0.130533 +-
0.021500
1.160275
0.276418
0.138608
5.455979
0.012954
1.162306
0.224300
1.646093
3.006824
0.525866
0.997576
0.086519
0.068054
0.249388
0.375063
1.111290
1.200914
0.430564
0.030416
0.012578
0.001842
0.093578
0.025989
0.006932
0.000565
0.001733
0.011912
0.003773
0.029246
0.001414
0.002089
0.001567
0.016490
0.002744
0.005106
0.004107
0.008231
0.009460
0.010358
0.012176
0.016401
0.017887
0.042704
0.071326
0.004689
0.070031
                             234
-------
Pacific Northwest Source Profile Project
SOURCE:
SPECIES
FLOR
DIBE
PHEN
ANTH
ACRI
CARB
FLUO
PYRE
RETE
BENB
BECP
CHRY
BEBF
BEEP
BAP
PERY
INDE
DIAA
BEGP
TETR
PENT
HEXA
HEPT
OCTA
NONA
TRIA
Hedco Hogged
FINE +-
0.000034 +-
0.000028 +-
0.000369 +-
0.000108 +•
0.000320 +-
0.000125 +-
0.000111 +-
0.000234 +-
0.000845 +-
0.000244 +-
0.000248 +-
0.000201 +-
0.000083 +-
0.000064 +-
0.000049 +-
0.000023 +-
0.000105 +-
0.000035 +-
0.000262 +-
0.000448 +-
0.000237 +-
0.001088 +-
0.001293 +-
0.000839 +-
0.000763 +-
0.001220 +-
Fuel Boiler
UNCERT COARSE +-
0.000026 +-
0.000029 +-
0.000255 +-
0.000108 +-
0.000231 +•
0.000132 +-
0.000053 +-
0.000160 +-
0.000817 +-
0.000249 +-
0.000238 +-
0.000150 +-
0.000077 +-
0.000035 +-
0.000039 +-
0.000025 +-
0.000109 +-
0.000038 +-
0.000185 +-
0.000480 +-
0.000229 +-
0.000780 +-
0.000759 +-
0.000639 +-
0.000610 +-
0.000857 +-
UNCERT PM-10
0.000034
0.000028
0.000369
0.000108
0.000320
0.000125
0.000111
0.000234
0.000845
0.000244
0.000248
0.000201
0.000083
0.000064
0.000049
0.000023
0.000105
0.000035
0.000262
0.000448
0.000237
0.001088
0:001293
0.000839
0.000763
0.001220
+- UNCERT
+- 0.000026
+- 0.000029
+- 0.000255
+- 0.000108
+- 0.000231
+- 0.000132
+- 0.000053
+- 0.000160
+- 0.000817
+- 0.000249
+- 0.000238
+- 0.000150
+- 0.000077
+- 0.000035
+- 0.000039
+- 0.000025
+- 0.000109
+- 0.000038
+- 0.000185
+- 0.000480
+- 0.000229
+- 0.000780
+- 0.000759
+- 0.000639
+- 0.000610
+- 0.000857
                             235
-------
Pacific Northwest Source Profile Project


LOCATION:Tacoma,  WA

SOURCE:  Residual Oil  Boiler
Profile:13502
DESCRIPTI          Fine data uses  filters  DTS143/DGS143, DTS145/DOS145,
and DTS147/DQS147.   Coarse data  uses DTS142/DQS142, DTS144/DQS144,
and DTS146/DQS146.
SPECIES     FINE   +-    UNCERT     COARSE   +-   UNCERT    PH-10     +-     UNCERT
F
CL
N03-
HP04-
S04=
NH4+
NA+
MG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
HO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
0.000000 +-
0.000000 +-
0.051933 +-
0.783533 +-
55
2
0
0
0
2
13
0
0
0
0
10
0
0
0
0
2
0
0
.041267 +-
.480033 +-
.383633 +-
.008300 +-
.031967 +-
.279133 +-
.557000 +-
.061967 +-
.120267 +-
.392700 +-
.072333 +-
.244800 +-
.052000 +-
.011667 +-
.114667 +-
.007200 +-
.354733 +-
.008633 +-
.002567 +-
0.107167 +-
0.001600 +-
1.043800 +-
0.002167 +-
0.010800 +-
0.000000 +-
0.001700 +-
0.012700 +-
0.000867 +-
0.000067 +-
0.002667 +-
0.000167 +-
6.000000 +-
0.000267 +-
0.000000 +-
0.000400 +-
0.001067 +-
0.000000 +-
0.000000 +-
0.
0.
0.
0.
0.
002567 +-
000300 +-
002933 +-
000433 +-
000000 +-
0.023350
0.051680
0.043562
0.259428
4
1
0
0
0
0
9
0
0
0
0
3
0
0
0
0
0
.679507
.264317
.107893
.008445
.019182
.959630
.347623
.066552
.039666
.123377
.353800
.694985
.015200
.002343
.021831
.023665
.485441
0.063804
0.006552
0.018574
0.002995
0.192297
0.004358
0.002886
0.003417
0.002659
0.004585
0.001208
0.001330
0.000665
0.001919
0.002519
0.004437
0.008455
0.
0.
0.
0.
0.
0.
0.
0.
0.
010007
010964
012924
017329
019146
068844
077062
004905
004424
0.000000 +-
0.141733 +-
0.110233 +-
0.000000 +-
8.358000 +-
0
0
0
0
3
74
0
0
.253833 +-
.085567 +-
.052433 +-
.009167 +-
.148333 +-
.246250 +-
.043333 +-
.423267 +-
0.913733 +-
0
10
0
0
0
0
1
.070867 +-
.577967 +-
.047867 +-
.010233 +-
.026200 +-
.007933 +-
.293800 +-
0.001967 +-
0.001600 +-
0.133100 +-
0.000867 +-
0.595300 «•-
0.001733 +-
0.002367 +-
0.004267 +-
0.000500 +-
0.002833 +-
0.000900 +-
0.000433 +-
0.001333 +-
0.001700 +-
0.
000000 +-
0.002767 +-
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
000000 +-
000000 +-
002167 +-
000000 +-
000000 +-
000000 +-
000000 +-
000000 +-
000900 +-
000000 +-
0.114050
0.253002
0.155893
0.308555
3
0
0
0
0
4
8
0
0
0
2
3
0
0
0
.676709
.073403
.130143
.073516
.032284
.618151
.780560
.105868
.219707
.339647
.189831
.822916
.032484
.021440
.022214
0.113458
0.252351
0.246400
0.025768
0.035968
0.012437
0.129689
0.017084
0.002840
0.016874
0.012789
0.003946
0.005955
0.006557
0.005986
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
009456
012466
021891
041959
049194
054413
064342
085885
094690
340187
379995
024160
021474
0.000000 +-
0.043000 +-
0.059100 +-
0.604467 +-
44
1
0
0
0
2
29
0
0
0
0
10
0
0
0
.227933 +-
.899800 +-
.306600 +-
.014233 +-
.025733 +-
.463800 +-
.404533 +-
.054167 +-
.176200 +-
.498033 *-
.070167 +-
.017800 •*•-
.049433 +-
.011400 +-
.093233 +-
0.007100 +-
2.073500 +-
0.006833 +-
0.002233 +-
0.110500 *-
0.001467 +-
0.925733 +-
0.001967 +-
0.008700 +-
0.000633 +-
0.001367 +-
0.010000 +-
0.000833 +-
0.000100 +-
0.002267 +-
0.000467 +-
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
000000 +-
000600 +-
000000 +-
000267 *-
001300 +-
000000 +-
000000 +-
001900 +-
000200 +-
002233 +-
000433 +-
000000 +-
0.029860
0.066296
0.059197
0.205143
7.192701
0.817358
0.053485
0.011477
0.014369
1.216988
11.256994
0.043693
0.045936
0.078908
0.539684
2.451996
0.008128
0.005221
0.012223
0.029782
0.285342
0.069462
0.007198
0.013092
0.003347
0.127158
0.004801
0.001558
0.004391
0.003358
0.002655
0.001577
0.001717
0.001362
0.002489
0.003250
0.005739
0.010929
0.012852
0.014123
0.016702
0.022381
0.024668
0.088573
0.099128
0.006341
0.005632
                            236
-------
Pacific Northwest Source Profile Project
SOURCE: Tacoma, UA Residual Oil Boiler
SPECIES FINE •+• UNCERT COARSE +- UNCERT PM-10 +-
FLOR
DIBE
PHEN
ANTH
ACRI
CARB
FLUO
PYRE
RETE
BENB
BECP
CHRY
BEBF
BEEP
BAP
PERY
INDE
DIAA
BEGP
TETR
PENT
HEXA
HEPT
OCTA
NONA
TRIA
0.000043 +-
0.000041 +-
0.000041 +-
0.000041 + -
0.000041 +-
0.000041 +-
0.000838 +-
0.001160 +-
0.006380 +-
0.000041 +-
0.000041 +-
0.000041 +-
0.000499 +-
0.000339 +-
0.000041 +-
0.000041 +-
0.000023 +-
. 0.000126 +-
0.000153 +-
0.037211 +-
0.051011 +-
0.076511 +-
0.129511 +-
0.072511 «•-
0.084511 +-
0.128511 +-
0.000047 +-
0.000045 +-
0.000045 +-
0.000045 +-
.0.000045 +-
0.000045 +-
0.000512 +-
0.000710 +-
0.003920 +-
0.000045 +-
0.000045 +-
0.000045 +-
0.000408 +-
0.000322 +-
0.000045 +-
0.000045 +-
0.000023 +-
0.000163 +-
0.000244 +-
0.054871 +-
0.074953 +-
0.112430 +-
0.190212 +-
0.106773 +-
0.124451 +-
0.188798 +-
0.000043 +-
0.000041 +-
0.000041 +-
0.000041 +-
0.000041 +-
0.000041 +-
0.000838 +-
0.001160 +-
0.006380 +-
0.000041 +-
0.000041 +-
0.000041 +-
0.000499 +-
0.000339 +-
0.000041 +-
0.000041 +-
0.000023 +-
0.000126 +-
0.000153 +-
0.037211 +-
0.051011 +-
0.076511 +-
0.129511 +-
0.072511 +-
0.084511 +-
0.128511 +-
UNCERT
0.000047
0.000045
0.000045
0.000045
0.000045
0.000045
0.000512
0.000710
0.003920
0.000045
0.000045
0.000045
0.000408
0.000322
0.000045
0.000045
0.000023
0.000163
0.000244
0.054871
0.074953
0.112430
0.190212
0.106773
0.124451
0.188798
PM-10 fraction assumed to be similar to fine fraction.
                           237
-------
Pacific Northwest Source Profile Project
LOCATION:  Simplot Co.  Pocatello,ID
SOURCE:   Gypsum
Profile: 27601
DESCRIPTION:       Sairple (NEA04)  collected on the north  side of
the gypsum pile.

SPECIES     FINE   +-    UNCERT     COARSE   +-    UNCERT     PH-10  +-    UNCERT
F -
CL -
N03-
HP04-
S04=
NH4+
NA+
HG+
K+
OC
EC
C03
AL
SI
P
S
CL
K
CA
TI
V
CR
HN
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
3.340800 +-
0.074100 +-
0.000000 +-
4.654600 +-
3.470700 +-
0.271500 +-
0.327800 +-
0.140500 +-
0.245900 +-
2.138200 +-
1.967200 +-
0.363000 +-
1.426000 +-
11.311900 +-
6.887000 +-
2.323100 +-
0.178400 +-
0.565200 +-
22.533900 +-
0.177400 +-
0.142000 +-
0.123900 +-
0.012400 -f-
0.851300 +-
0.001300 +-
0.020000 +-
0.031400 +-
0.159700 +-
0.000000 +-
0.001500 +-
0.010000 +-
0.002800 +-
0.002100 +-
0.121900 +-
0.042800 +-
0.013900 +-
0.006000 +-
0.000000 +-
0.004000 +-
0.016100 +-
0.000000 +-
0.002100 +-
0.000000 +-
0.001300 +-
0.028300 +-
0.003700 +-
0.005500 +-
0.243600 4.547000 +-
0.035200 0.000000 +-
0.015200 0.106400 +-
0,355900 2.487400 +-
0.249400 25.430400 +-
0.063000 0.089300 +-
0.025300 0.214600 +-
0.011300 0.071700 +-
0.021200 0.170400 +-
1.842800 1.433500 +-
0.811100 1.898800 +-
0.088100 0.016200 +-
0.130300 2.015400 +-
0.822300 9.720000 +-
0.492000 3.655700 +-
0.165900 13.574300 +-
0.016100 0.198900 +-
0.090600 0.456600 +-
1.606300 25.054000 +-
0.017300 0.118600 +-
0.011700 0.054000 +-
0.009300 0.043800 +-
0.002100 0.007600 +-
0.060900 0.469000 +-
0.012600 0.002300 +-
0.001600 0.008700 «•-
0.002400 0.009800 +-
0.011500 0.068600 +-
0.004200 0.000000 +-
0.004300 0.001800 +-
0.001100 0.004600 +-
0.000700 0.001000 +-
0.001600 0.003500 +-
0.008800 0.159500 +-
0.003300 0.028300 +-
0.002400 0.008300 +-
0.006500 0.002200 +-
0.012900 0.006700 +-
0.015800 0.009200 +-
0.017300 0.015200 +-
0.019400 0.002700 +-
0.026600 0.000800 +-
0.029600 0.000700 +-
0.104100 0.059900 +-
0.119300 0.025900 +-
0.007400 0.002100 +-
0.006300 0.002400 +-
0.462800 4.193800
0.028700 0.020000
0.015800 0.075200
0.324400 3.122000
2.355000 19.000200
0.051100 0.142700
0.026200 0.247700
0.009900 0.091800
0.021800 0.192500
1.519800 1.639900
0.687700 1.918900
0.070200 0.117700
0.656600 1.842800
3.292900 10.186100
1.615800 4.601900
4.838100 10.279700
0.062400 0.192900
0.173600 0.488400
4.833100 24.316100
0.017300 0.135800
0.009300 0.079800
0.006900 0.067200
0.001900 0.009000 •
0.057400 0.580900
0.013200 0.002000 •
0.001300 0.012000 •
0.001700 0.016100 •
0.009200 0.095200 •
0.003600 0.000000 •
0.003800 0.001700 •
0.000900 0.006200 -
0.000600 0.001500 •
0.003400 0.003100 ^
0.016300 0.148500 -
0.003400 0.032500 n
0.003400 0.009900 H
0.005600 0.003300 H
0.011400 0.004700 <
0.013800 0.007700 n
0.008600 0.015500 <
0.016900 0.001900 <
0.022800 0.001200 H
0.025700 0.000500 <
0.090200 0.042800 ^
0.102300 0.026600 H
0.006400 0.002600 ^
0.005500 0.003300 ^
+- 0.302900
+- 0.017500
+- 0.009400
+- 0.233800
+- 1.367100
+- 0.031800
+- 0.018500
+- 0.007100
+- 0.015100
+- 0.930700
+- 0.424700
+- 0.043100
+- 0.460400
+- 2.323100
+- 1.146000
+- 3.384600
+- 0.043800
+- 0.120300
+- 3.367100
+- 0.011800
*- 0.006700
+- 0.005100
*•- 0.001300
«•- 0.041900
*- 0.008600
*- 0.000900
••- 0.001300
«•- 0.006900
f- 0.002300
i- 0.002300
<•- 0.000600
i- 0.000300
H- 0.002300
>" 0.010700
H- 0.002400
i- 0.002300
i- 0.003500
>•- 0.007100
I- 0.008600
>•- 0.003300
i- 0.010500
i- 0.014100
>- 0.016000
- 0.056000
- 0.063400
•- 0.004000
•- 0.003400
                                 238
-------
13-Jun-8S
                                                  SOURCE LIBRARY
            SOURCE:   FEED AND GRAIN HANDLING DUST.
            SCC:       3-02-005-01
            CONTROLS:  UNKNOWN
PROFILE:     21401
RANKING:   UNKNOWN
RATING :         D
SPECIE
NUMBER
4
5
9
11
12
13
14
15
16
17
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
34
35
37
38
40
47
48
50
51
55
56
58
80
82
200
202
203
204
SUMC X )
SPECIE
NAME
BE
B
F
NA
MG
AL
SI
P
S
CL
K
CA
SC
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
GE
AS
SE
BR
R8
SR
ZR
AG
CD
SN
SB
CS
BA
CE
HG
PB
TC
EC
S04
N03

*********
X BY UT
NA
NA
NA
NR
NR
NR
15.000
<
<
<
0.550
0.550
<
<
<
<
<
0.050
<
<
0.050
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
30.000
NA
0.550
NA
46.750
FINE
<2.5 UM ******
+ - UNC
* - NR
+ • NR
+ • NR
* • NR
+ • NR
+ • NR
+ - NR
+ - NR
+ - NR
+ • NR
* - NR
* • NR
+ • NR
4- • NR
* - NR
+ • NR
+ • NR
+ • NR
+ • NR
+ • NR
+ • NR
* • NR
* • NR
* - NR
+ • NR
4- • NR
+ • NR
* - NR
+ • NR
+ - NR
+ • NR
+ • NR
+ • NR
+ • NR
4- • NR
4- - NR
•f • NR
+ • NR
4- • NR
+ • NR
+ - NR
+ • NR
+ - NR

*********
X BY UT
NA
NA
NA
NR
NR
NR
15.000
<
<
<
0.550
0.550
<
<
<
<
<
0.050
<
<
0.050
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
30.000
NA
0.550
NA
46.750
COARSE
2.5-10UM ******
4- UNC
+ • NR
+ • NR
+ • NR
+ • NR
+ - NR
+ - NR
4- • NR
+ • NR
4- • NR
+ - NR
+ • NR
4- - NR
+ • NR
+ - NR
4- - NR
+ - NR
* - NR
+ - NR
+ • NR
+ - NR
+ - NR
4- • NR
+ - NR
+ - NR
+ - NR
+ • NR
«• - NR
+ • NR
+ - NR
4- • NR
+ - NR
+ - NR
* • NR
+ • NR
4- • NR
+ • NR
+ • NR
+ - NR
•f - NR
+ - NR
+ - NR
+ - NR
+ - NR

*********
X BY UT
NA
NA
NA
NR
NR
NR
15.000
<"
<
<
0.550
0.550
<
<
<
<
<
0.050
<
<
0.050
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
<
30.000
NA
0.550
NA
46.750
TSP
<30 UM ******
4- UNC
* • NR
+• • NR
+ - NR
+ - NR
+ - NR
+ •' NR
+ - NR
+ • NR
+ - NR
+ - NR
* - NR
+ - NR
+ • NR
* - NR
* - NR
4- - NR
4- - NR
4- - NR
4. • NR
4- - NR
+ - NR
4- - NR
+ - NR
4- - NR
4- • NR
4- • NR
* • NR
4. - NR
* - NR
+ - NR
4- - NR
4- - NR
+ - NR
+ • NR
4- - NR
4- - NR
+ - NR
* - NR
4- - NR
+ • • NR
4- - NR
4- - NR
+ • NR

   NOTES:   OC » ORGANIC CARBON :  EC = ELEMENTAL CARBON      NR:  NOT  REPORTED
            < = LESS THAN DETECTION LIMIT   •         :   NA * NOT ANALYZED
            OTHER NOTES :      SOURCE TEST, ANALYTICAL  METHODS AND REPRESENTATIVENESS
             REF: 10           OF THE DATA UNKNOWN BUT  LIKELY OF POOR  QUALITY.
                                                 239
-------
13-Jun-85
                                                 SOURCE LIBRARY
SOURCE: CAST IRON CUPOLA
SCC: 3-04-003-01
CONTROLS: UNSPECIFIED

SPECIES
NUMBER
4
5
9
11
12
13
14
15
16
17
19
20
21
22
23
24
25
26
27
23
29
30
31
32
33
34
35
37
38
40
47
48
50
51
55
56
53
80
82
201
202
203
204
SUM( X )
FINE COARSE
NAME X BY UT + • UNC X BY WT +• UNC
BE + - + •
B + • + •
F + - + -
NA + - +
MG + +
AL + - + •
SI + - * -
p + - + -
s + - + -
CL * - + -
K + - + -
CA + + -
SC + - + -
TI + - +
V + - + -
CR + - + -
MM + - «• -
FE + - + •
CO + - * -
MI + - + •
CU + - + •
ZM + - + -
GA + • + •
GE + • > -
AS + • + -
SE + • + •
BR + • -f -
RB * • + •
SR + • + •
ZR + • + •
AG + + -
CD + - + -
SN + - + -
SB + - + •
CS + - + -
BA + - + -
CE + - + •
HG + - + •
PB + - + -
OC + - * •
EC + • + •
S04 + - + -
N03 + - * -
0.000 0.000
PROFILE: 28202
RANKING: 1324
RATING : C
TSP

X BY WT +- UNC
NA +
NA +
NA +
1.300 + •
< +
1.100 +
24.000 t •
< +
2.300 + -
0.890 + -
3.000 +
1.000 +
< -f
0.060 +
0.009 + •
0.052 + -
4.500 + -
15.000 * -
0.004 + -
0.035 + -
0.260 + -
0.830 + -
< + -
< + -
0.013 «• •
0.002 + •
0.009 + -
0.022 + -
< + -
< + -
< + •
< + -
< + -
0.370 + -
< +
< + -
< + -
< + •
0.230 + -
NA + •
NA + •
NA •*• •
NA + -
52.686
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR

   NOTES:   OC - ORGANIC CARBON  :   EC = ELEMENTAL CARBON
            < = LESS THAN DETECTION LIMIT
            OTHER NOTES : REF. 47.
NA - NOT ANALYZED :   NR = NOT  REPORTED
                                                  240
-------
13-Jun-85
SOURCE LIBRARY
SOURCE:
SCC:
CONTROLS:
SPECIES
NUMBER
4
5
9
11
12
13
14
15
16
17
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
34
35
37
38
40
47
48
50
51
55
56
58
80
82
201
202
203
204
SUM( X )
SPECIES
NAME
BE
B
F
NA
MG
AL
SI
P
S
CL
K
CA
SC
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
GE
AS
SE
BR
RB
SR
ZR
AG
CD
SN
SB
CS
BA
CE
HG
PB
OC
EC
S04
N03

SOIL OUST •
NONE
NONE
*********
X BY UT
NA
NA
NA
NA
1.280
11.120
27.336
0.336
0.380
0.024
0.719
0.864
<
0.440
0.039
<
0.144
4.989
<
<
0.008
0.042
<
<
<
<
<
<
0.021
<
<
0.039
<
<
<
<
<
<
0.107
NA
NA
NA
NA
47.888
• SEATTLE, WASHINGTON
PROFILE: 41302
RANKING: 3334
RATING : C
FINE COARSE TSP
<2.5 UM ****** ********* 2.5-10UM ****** ********* <3Q JJM ******
+ • UNC X BY UT *• UNC X BY WT +• UNC
+ - NR + •
* - NR + •
+ • NR * •
+ • NR + •
+ • 0.108 + -
+ - 0.743 * -
* - 1.780 * -
+ - 0.031 + •
+ - 0.088 + •
+ - 0.035 * -
+ - 0.066 + -
* • 0.070 * -
+ - NR * •
+ - 0.038 + •
+ - 0.009 * -
+ - NR + -
+ • 0.014 + -
+ - 0.340 + -
* • NR + •
+ • NR + •
+ - 0.006 + -
* • 0.008 + •
+ • NR * •
+ - NR + •
* - NR «• •
+ • NR + •
* - NR + •
+ • NR + •
+ - 0.008 + •
* • NR * •
+ • NR + •
+ • 0.055 * •
+ • NR + -
* • NR * •
* - NR + •
* - NR * •
+ • NR + •
* - NR * -
+ - 0.022 + -
+ • NR + •
+ - NR + •
•f - NR + •
+ - NR + •
0.000
+ .
•f -
+ -
+ -
* -
+ •
+ -
+ -
•f -
•f •
+ -
+ -
* -
+ •
+ -
+ -
+ -
+ -
+ •
» •
* •
* -
+ •
+ -
* -
* -
+ •
* •
+ -
•f •
* •
+ •
+ •
* •
+ •
+ -
+ •
+ -
+ -
+ •
* -
+ •
+ -
0.000
   NOTES:    OC => ORGANIC CARBON :   EC = ELEMENTAL  CARBON  :  NA = NOT ANALYZED  :  NR <= NOT REPORTED
            < = LESS THAN DETECTION LIMIT
            OTHER NOTES :      RESUSPENDED LOCAL SOIL  SAMPLES, FINE FRACTION,  ONLY. EACH ANALYZED
                               SAMPLE IS A COMPOSITE OF THREE SOIL SAMPLES. REF. 27
                                                    241
-------
SOURCE: Cement Dust Fugitives                      Profile:  SCAQMD  51





DESCRIPTION: Cement Dust (SRM 633);  South  Coast  AQMD  Profiles.





SPECIES    FINE   +-  UNCERT   COARSE   +-   UNCERT     PM-10   +-   UNCERT
F
CL
N03-
HP04-
S04=
NH4+
NA+
MG+
K+
OC
EC
C03
AL
SI
P
S
CL
K.
CA
TI
V
CR
MM
FE
CO
NI
CU
ZN
GA
AS
SE
BR
RB
SR
Y
ZR
MO
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
2.0000 +-
10.2000 +-
0.1000 + -
0.0001 +-
NR +-
0.0000 +-
46.1000 +-
' 0.1400 +-
NR +-
0.0070 +-
0.0300 +-
2.9400 +-
NR +-
NR +-
NR +-
0.0080 +-
NR +-
NR +-
NR +-
NR +-
NR +-
0.2600 +-
NR +-
NR +-
NR + -
NR +-
NR +-
NR +-
NR +-
NR + -
NR +-
NR +-
NR +-
NR +-
NR +-
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.4000
2.0000
0.0200
0.0000
NR
0.0000
4.6100
0.0280
NR
0.0010
0.0060
0.5800
NR
NR
NR
0.0033
NR
NR
NR
NR
NR
0.0520
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR +-
NR +-
NR +-
NR +-
NR +r
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
2.0000 +-
10.2000 +-
0.1000 +-
0.0001 +-
NR +-
0.0000 +-
46.1000 +-
0.1400 +-
NR +-
0.0070 +-
0.0300 +-
2.9400 +-
NR +-
NR +-
NR +-
0.0080 +-
NR +-
NR +-
NR +-
NR +-
NR +-
0.2600 +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.4000
2.0000
0.0200
0.0000
NR
0.0000
4.6100
0.0280
NR
0.0010
0.0060
0.5800
NR
NR
NR
0.0033
NR
NR
NR
NR
NR
0.0520
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +•
NR +-
NR +-
NR +-
NR +-
NR +-
2.0000 +-
10.2000 +-
0.1000 +-
0.0001 +-
NR +-
0.0000 +-
46.1000 +-
0.1400 +-
NR +-
0.0070 +-
0.0300 +-
2.9400 +-
NR +-
NR +-
NR +-
0.0080 +-
NR +-
NR +-
NR +-
NR +-
NR +-
0.2600 +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR +-
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
0.4000
2.0000
0.0200
0.0000
NR
0.0000
4.6100
0.0280
NR
0.0010
0.0060
0.5800
NR
NR
NR
0.0033
NR
NR
NR
NR
NR
0.0520
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR = Not Reported.Data  from NBS Standard Reference Material
                            242
-------
Appendix D-3.  Kaiser Emission Data
Three different sets of source tests numbers from Kaiser are presented on Enclosure A. The
first set consists of columns A and A' (Ecology 1985).  To get a total emission from Kaiser for
each constituent the value in column A is doubled and added to the value in column A'. The
reason for doubling column A is that only line 4 was tested which accounts for only-half of the
roof monitor emissions.

The second  set consists of columns B and B' (Kaiser  1985). To get a total emission for each
constituent again column  B is doubled and added to column B'.  It should be noted that sets A
and B are two different sets of analyses on the same source test  data (A-A' by Ecology and B-
B' by Kaiser).  The source test was performed by Ecology.

The third set of numbers consists of columns C, C',C", and D (AMTEST 1988).  The total
emissions for each constituent is  acquired by adding the four columns.

Table A  on  Enclosure B  contains the results of the  manipulations described above.  This then
can be considered a range of possible emission numbers for Kaiser.  Table B is the sum of the
source test information presented in Table A for Ecology and Kaiser plus the 1988 paste plant
emissions.  The reason for considering  this sum is that the paste plant was not tested in 1985.

Another  iteration of the source test numbers would  be to double column C" for the AMTEST
totals as  the numbers in column  C" are based on 50% of the potential ore feed for the plant.
However, Kaiser assures us that  50% ore feed represents normal operation.
                                          243
-------
                                                                             ENCLOSURE A
Emissions of PAHs from Kaiser-Tacoma. Grams/Hour
Mol. Potency
COMPONENT
Naphthalene
Acenaphthylene
Acenaphthene
Fluorene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a)Anthracene
Chrysene
Benzo(b)Fluoranthene
Benzo(k)Fluoranthene
Benzo(a)Pyrene
Indeno(l ,2,3~c,d)Pyrene
Dibenzo(a,h)Anthracene
Benzo(g,h,i) Perylene
Benzo(e)Pyrene
Dibenzo(a,e)Pyrene
Dibenzo(a,i)Pyrene
Dibenzo(a,h)Pyrene
Wt.
128
152
154
166
178
178
202
202
228
228
252
252
252
276
278
276
252
302
302
302
A
[
[
Sep85
B C1 C"
MONITORS ]
Line 4 ] [Lnl&2]
Sep85 M88 M88
Factor WDOE KACC AmTest AmTest
*
*
.320
*
*
0
0
.081
.145
.004
.140
.066
1.000
.232
1.100
.022
.004
*
*
*
258
96
1060
170
1139
80
791
519
131
259


125







201
181
24
113
1585
181
937
945
124
341


89







47
2
22
25
424
19
208
116
22
60
27
14
8
5
2
5
14
0
0
0
36
3
24
24
323
17
187
114
24
70
31
16
6
5
3
5
16
0
0
0
A' B' C"
[ DRY SCRUBBERS
50%
Sep85 Sep85 M88
WDOE KACC AmTest
2286
250
3914
3914
3266
2944
1882
1354
100
64


52







604
94
1726
1726
2510
4814
1040
1052
16
40


2







8381
95
1693
1693
7055
507
897
618
7
13
0
0
0
0
0
0
0
0
0
0
D
]
Paste
Plant
M88
42
0
202
202
111
2
2
1
0
0
0
0
0
0
0
0
0
0
0
0
Total

* Potency Factors not listed
"0" indicates not detected
 4628   4721
       1020
903
17530  13148   20429   403
Grams of B(a)p Equivalent Potency        144

Totals for PLANT          WDOE*  KACC*
Total PAHs, Grams/Hr        27189
Total B(a)p Equiv., Gm   /Hr     355

* Paste plant added
22993
  220
108      18

   Amtest88

      22754
         36
                         18
          66
                                            244
-------
                                                                ENCLOSURE B

Table A. PAH Emissions from Kaiser-Tacoma, grams/hour	

                                 ECOLOGY           KAISER          AMTEST
CHEMICAL COMPONENT	(1985)	(1985)	(1988)

Naphthalene                            2802              1006              8506
Acenaphthylene                          442               456               100
Acenaphthene                          6034              1774              1941
Fluorene                              1758              1476              1256
Phenanthrene                           5544              5680              7913
Anthracene                             3104              5176               545
Fluoranthene                           3464              2914              1294
Pyrene                                2392              2942               849
Benzo(a)anthracene                       362               264                53
Chrysene                               582               722               143
Benzo(b)fluoranthene                      	                	                58
Benzo(k)fluoranthene                      	                	                30
Benzo(a)pyrene                          302               180                14
Indeno(l,2,3-c,d)pyrene                    	                	                10
Dibenzo(a,h)anthracene                    	                	                 5
Benzo(g,h,i)perylene                      	                	                10
Benzo(e)pyrene                           	                	                30
Table B. PAH Emissions from Kaiser-Tacoma, grams/hour (sum of 1985 monitor and dry
scrubber emissions in Table A plus 1988 paste plant emissions)	

CHEMICAL COMPONENT	ECOLOGY	KAISER	

Naphthalene                             2844              1048
Acenaphthene                           6236              1976
Fluorene                               1801              1519
Phenanthrene                            5655              5791
Anthracene                             3106              5178
Fluoranthene                            3466              2916
Pyrene                                 2393              2943


Note: The sums in Table B include only those compounds for which paste plant emissions were
available.
                                      245
-------
Appendix D-4.  Simpson Tacoma Kraft Source Test
                                     247
-------
Appendix D-4(a). Sampling Protocol
Sampling Equipment

A size-segregating dilution sampler (SSDS) was used to collect paniculate samples from three
emission points at the Simpson plant. The dilution sampler consists of three main components:
a probe, a dilution chamber, and a particle collector. The sampling probe is connected to the
stack wall with port flanges whenever possible.  Unlike compliance tests, the  sampling probe
is fixed at one position throughput the entire test cycle.   A particle preseparator on the front
end of the probe regulates the size of particulates (650=10 pm) entering the dilution chamber.

The dilution chamber is constructed of stainless steel, four-inch-diameter tubing held in place
with quick-connect clamps.   Ambient air is filtered through a quartz fiber filter  (Whatman
QMA) before entering  the dilution chamber to mix with the stack gas sample.  Blowers on the
inlet and outlet of the dilution chamber  regulate the pressure drop between the stack and
chamber that is required  to withdraw the stack sample and regulate the ratio of dilution air to
stack sample.

The diluted stack emissions were collected on two 37-mm Teflon (Gelman R2PJ037) filters and
two 37-mm quartz fiber (Pallflex QAT-UP) filters simultaneously. Two Andersen Model 244
dichotomous  samplers  with  modified inlet tubes were used to collect  both fine  (less than
2.5 urn) and  coarse (2.5 to  10 /xm)  samples from the dilution chamber.  The excess diluted
emissions were collected on an 8- by 10-inch-outlet quartz fiber filter (Pallflex QAT-UP).

All of the source tests included three replicate runs of the SSDS.  A total  of 12 filters were
collected for each of the source tests.  Each set contained three fine-fraction samples on Teflon
filters and three fine-fraction samples on quartz filters.

Discussion of Sources and Sampling Conditions

All of the sources tested  at the Simpson Tacoma Kraft facility were operating under "normal"
conditions.  Close communication was maintained throughout the testing cycle with the plant
operators to assure constant operating conditions.

Hogged Fuel Boiler

The north scrubber hogged fuel boiler was tested on January 2 and 3, 1990.  The plant operator
reported that sludge was mixed with the hogged fuel and that the hogged fuel was of low grade
(high moisture content, possibly including old bark and/or sea water, sand and dirt) during the
test duration.  Samples of the fuel mixture were not collected during this project.

Four separate boilers (Nos. 2, 3, 4, and 5) are ducted to the north scrubber  stack.   Variability
in  steam production from  any one of  the three boilers may  not directly influence the
performance of the scrubber.  The scrubber produced a super-saturated plume at temperatures
between 120 and  130°F. The stack flow rate was monitored throughout the test cycle and
remained fairly constant at six meters/second at the test port level.

The dilution sampling at the hogged fuel boiler ran with little or no problems. A target dilution
ratio of 15:1 was chosen at the start of the  test because of the high moisture content of the stack
gas. The average dilution for all three runs was approximately 10:1 for runs 1 and 2; a lower
mixing  rate was used  for run 3 in order  to decrease the sample duration.  The filters were
checked intermittently during the test to monitor for condensation in the chamber, and none was
observed.


                                          249
-------
Lime Kiln

The No. 1 lime kiln stack was sampled on January 4, 1990. The dilution sampler was set up
on  the  platform approximately  six  feet below  the  level of the compliance test ports and
downstream of the scrubber.  This site was selected because of insufficient space and physical
obstructions on the level above.  Lime kiln No. 1 is the main production kiln while the No. 2
lime kiln is used less frequently and has  a lower capacity.  The emissions from the No.  1 lime
kiln are ducted through a scrubber which produces a highly saturated plume with a temperature
range of 160 to 180°F.

Process operation data from the kiln were provided by Simpson.  No bulk samples of the fuel
that was used or the scrubber water were collected by the sampling crew.

All three tests were completed in one day with the runs ranging from 40 minutes to 1.5 hours.
Although target dilution ratio of 10:1 was chosen at the start of the test, the actual dilution ratio
varied from 20:1 to 22:1.

Water droplets were observed on the coarse fraction Teflon filter during run No. 2. Corrective
action was taken to remove the moisture  from the dilution chamber and to prevent condensation
from recurring.  Apparently, the dilution ratio was too low for the present  stack and ambient
conditions.

Recovery Furnace

The west scrubber stack of the No. 3 recovery furnace was sampled on January 5, 1990.  The
emissions from the recovery furnace are initially  controlled by an electrostatic precipitator and
then by scrubbers  before being vented out two stacks.  The sampling site was downstream of
the scrubbers and  the stack diameter at  this location  was approximately nine feet. The stack
temperatures ranged from 147 to 154°F, and the plume was super-saturated.  The field crew
did not collect any bulk samples of the  scrubber water or the black liquor from the recovery
furnace operation.

The three replicate runs of the SSDS had sample durations ranging from two to three hours.
The dilution ratio  was approximately 10:1 for all three runs.

The percent isokinetic rate is indicative of the extraction efficiency of the sample from the stack
gas.  Ideally, a source tester strives for 100  +. 10  percent isokinetics, which results in an
unbiased sample for the distribution of  fine and coarse particles.  Deviating from this range
results  in an enrichment of either fine  or coarse  particles.  However, this is not always a
practical application in wet or saturated stream flows where the water droplets can interfere with
the particle flow.  Moreover, the particle preseparator  on the front end of the probe requires
a constant flow rate in order to provide the desired cutpoint (Dx = 10 pm).   This requirement
will take precedent over the isokinetic rate when fluctuations occur in the stack velocity or when
nozzle sizing is limited. The deviation  from isokinetic range becomes less  significant in this
project because only the samples containing fine particles were analyzed.  The deviations should
not influence the  relative chemistry of fine particles.

Dr. Dave Kalman at the University of  Washington performed the organic  speciation for the
Simpson Tacoma Kraft study.  Samples collected by NBA at the Simpson mill were analyzed
for organic and elemental carbon before being sent to Dr. Kalman for further organic analysis.
                                          250
-------
Quality Assurance

Standard operating procedures were followed whenever possible for the handling, preparation,
sampling, and analysis of the samples collected from Simpson Tacoma Kraft.

Source Testing

The dichotomous sampler rotameters  were calibrated before the study and then adjusted to the
local  ambient conditions  in order to  maintain  the proper  flow rates  through the virtual
impactors.  The SSDS was thoroughly  cleaned before the  study and  sealed  to minimize
contamination during transport.  The  SSDS was also cleaned between each emission source to
prevent cross-contamination.

Analytical

Quality assurance reports signed by NEA's quality assurance manager were submitted with each
analytical report.  The quality assurance reports were submitted along with the analytical results
under separate cover to the Puget Sound Water Quality Authority.

Sample Preparation and Handling

Filters received from the lab were loaded  into labeled dichotomous cassette rings and stored in
Petri dishes which were also labeled  with the sample identification number.

A field transport box was used to carry the filters  to and from the sampling platforms from
which they  were loaded into the SSDS.  The samples were  then returned to the laboratory,
logged in, and unloaded from  the  dichotomous cassette rings into labeled Petri  dishes.  The
samples were then refrigerated at 4°C until each analysis was performed.

Samples with potential problems were identified. The problem samples, which were all coarse
fraction  samples, were  not used for any chemical analyses.  The  samples were identified
through problems noted in the field and by discrepancies in total mass.  The variations in mass
between Teflon and quartz filters can be  caused  by a number of different factors.  The
uncertainty associated with weighing  quartz filters is several times higher than the uncertainty
associated with Teflon filters. Fiber loss and absorption of water vapor are two factors that will
significantly impact the variability of the quartz mass.
                                         251
-------
Appendix D-4(b).  Laboratory Protocols
The laboratory protocols for the Simpson Tacoma Kraft source test are available on request
from Puget Sound Water Quality Authority (PS WQ A), contained in Appendix D. of NBA, Inc.,
Simpson Tacoma Kraft Emission Testing, Size-Segregating Dilution Sampling Report, prepared
for PSWQA, April 10,  1990.
                                         253
-------
Appendix D-4(c). PAH Results-University of Washington
                                      255
-------
    Appendix D-4(c).  Source Samples: Wt Percent - PAH
K
HOG FUEL HOG FUEL HOG FUEL LIMEKILN LIMEKILN RECOV FURN. RECOV FURN. RECOV FURN.

Fraction Analyzed
Deposit Mass pg/filter
Mass Analyzed(total) pg
Organic Mass Anal, ng
COMPOUND
detection limit
lower quantitation limit
21 FLUORENE
22 DIBENZOTHIOPHENE
23 PHENANTHRENE
24 ANTHRACENE
25 ACRIDINE
26 CARBAZOLE
27 FLUORANTHENE
28 PYRENE
29 1,2-BENZOFLUORENE
30 RETENE
31 BENZO(B)NAPTHO(1,2-D)THIOPHENE
32 BENZO(C)PHENANTHRENE
33 CHRYSENE
35 BENZO(B-f-K)FLUORANTHENE
36 BENZO(E)PYRENE
37 BENZO(A)PYRENE
38 PERYLENE
40 INDENO(1,2,3-C,D)PYRENE
41 DIBENZ(A,H)ANTHRACENE
42 BENZO(GHI)PERYLENE
43 TETRACOSANE
44 PENTACOSANE
45 HEXACOSANE
46 HEPTACOSANE
47 OCTACOSANE
48 NONACOSANE
49 TRIACONTANE
M0491
0.47
291
136.77
2.9
WT %
7.3E-04
1.5E-03
<
<
<
<
<
2.7E-03
1.5E-03
1.1E-03
<
1.8E-03
<
<
<
<
<
<
<
<
<
<
2.7E-03
1.9E-03
1.2E-03
1.3E-03
<
<
<
M0493
0.502
663
333
11.9
WT %
3.0E-04
6.0E-04
<
<
6.2E-04
3.5E-04

3.2E-03
1.7E-03
1.6E-03
<
5.1E-03
<
3.1E-04
5.8E-04
7.0E-04
5.4E-04
5.6E-04
<
<
<
<
<
2.0E-03
l.OE-03
<
<
<
<
M0495 M0499
1 1
450 866
450 866
5.5 0.0
WT % WT %
2.2E-04 1.2E-04
4.4E-04 2.3E-04
< <
2.4E-03 <
8.0E-04 <
< <
2.8E-04 <
2.4E-03 <
2.3E-03 <
2.0E-03 <
3.3E-04 <
9.9E-04 <
< <
< <
4.0E-04 <
< <
< <
< <
< <
< <
< <
< <
< <
< <
< <
< <
< <
< <
< <
M0501 M0503
1 1
852 853
852 853
8.4 10.2
WT % WT %
1.2E-04 1.2E-04
2.3E-04 3.7E-04
< <
< <
< <
< <
< <
< 5.2E-04
< <
< <
< <
< 5.9E-04
< <
< <
< <
< <
< <
< <
< <
< <
< <
< <
< 8.0E-04
< 8.9E-04
< 5.4E-04
2.5E-04 5.2E-04
2.0E-04 2.4E-04
< <
< 1.2E-04
M0505
1
535
535
9.7
WT %
1.9E-04
3.7E-04
<
<
<
<
<
3.4E-04
2.3E-04
<
N.A.
N.A.
<
<
<
<
<
<
<
<
2.0E-04
<
2.9E-04
<
1.3E-03
1.5E-03
3.2E-04
<
<
M0507
0.52
508
264.16
6.1
WT %
3.8E-04
7.6E-04
<
<
<
<
6.1E-04
<
<
<
<
3.1E-03
<
<
<
<
<
<
<
<
<
<
1.7E-03
1.7E-03
8.9E-04
8.1E-04
<
<
<
     1 < " INDICATES LESS THAN THE STATED DETECTION LIMIT VALUE; VALUES IN BOLD ARE ESTIMATED BELOW THE LOWER QUANTTTATION LIMIT
-------
Appendix D-4(d).  Metals Results - NEA
                                      259
-------
Analysis Summary, 298/01, Hog Fuel Boiler, Particle Size: F
Element
F
NA
MG
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
GE
AS
SE
BR
RB
SR
Y
ZR
MO
TC
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
OC
EC
NO3
NH4
PO4
S04

V/NI
BR/PB
Maximum Minimum
Percent Percent
.000
26.632
.078
.391
.435
.104
12.091
36.378
13.104
.468
.024
.404
.007
.047
.276
.005
.320
.052
.735
.004
.000
.049
.000
.135
.021
.004
.004
.000
.021
5.737
.007
.017
.034
.011
.053
.073
.044
.197
.002
.294
2.774
2.963
.377
1.677
.890
32.984
Mean
1.197
.402
.000
26.084
.000
.000
.000
.070
8.343
21.550
12.394
.275
.010
.065
.002
.029
.234
.000
.055
.045
.455
.000
.000
.018
.000
.043
.012
.000
.000
.000
.000
3.296
.000
.000
.000
.000
.000
.000
.000
.022
.000
.202
1.768
1.528
.000
.000
.225
23.382
SD
.059
.231
Mean
Percent
.000
26.404
.052
.241
.237
.087
9.732
26.903
12.741
.366
.018
.182
.004
.037
.258
.002
.148
.049
.607
.002
.000
.032
.000
.099
.017
.002
.001
.000
.013
4.514
.002
.006
.018
.004
.018
.033
.015
.085
.001
.262
2.344
2.169
.241
1.073
.581
26.834
N
3
3
Mean
Unc.
.190
2.744
.081
.044
.037
.027
1.134
2.152
1.019
.064
.003
.012
.003
.003
.017
.003
.010
.004
.035
.002
.001
.015
.001
.006
.003
.003
.003
.006
.011
.896
.009
.011
.015
.016
.020
.035
.148
.120
.003
.018
.815
.540
.124
.210
.061
2.794



SD
.000
.286
.045
.211
.220
.017
2.054
8.229
.355
.097
.007
.192
.002
.009
.021
.002
.149
.003
.142
.002
.000
.016
.000
.050
.005
.002
.003
.000
.011
1.221
.004
.009
.017
.007
.031
.037
.026
.097
.001
.052
.519
.730
.209
.931
.335
5.339



N
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3



Mean
ng/m3
.000
94.502
.141
.828
.667
.296
32.193
98.670
46.182
1.400
.071
.395
. .011
.142
.897
.010
.329
.173
2.379
.004
.000
.095
.001
.348
.055
.006
.002
.000
.034
14.964
.003
.009
.048
.020
.022
.149
.079
.175
.003
1.012
8.034
6.930
1.155
5.092
1.645
89.114



Mean
Unc.
.529
13.456
.315
.178
.131
.094
4.884
12.434
5.820
.270
.012
.047
.008
.018
.104
.008
.039
.021
.270
.005
.004
.058
.004
.040
.011
.007
.008
.017
.032
3.056
.025
.031
.044
.045
.056
.099
.411
.338
.009
.118
2.508
1.746
.286
.847
.234
12.690



SD
.000
55.418
.169
1.102
.744
.169
16.136
64.397
28.056
.923
.051
.112
.005
.092
.490
.009
.085
.098
1.697
.003
.000
.048
.001
.320
.032
.007
.003
.000
.039
8.534
.005
.010
.052
.035
.037
.155
.137
.075
.006
.680
4.958
3.577
1.037
4.445
.875
44.838



N
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3



                                       261
-------
Analysis Summary, 298/01, Lime Kiln, Particle Size: F
Maximum Minimum
Element Percent Percent
F
NA
MG
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
GE
AS
SE
BR
RB
SR
Y
ZR
MO
TC
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
OC
EC
NO3
NH4
P04
S04

V/NI
BR/PB
.000
33.626
.308
.267
.081
.242
15.549
2.449
1.154
6.490
.019
.079
.006
.051
.579
.005
.022
.019
.014
.002
.000
.004
.001
.004
.000
.016
.000
.004
.008
1.184
.005
.007
.000
.007
.010
.010
.097
.069
.000
.879
.605
.578
.078
.000
.381
56.468
Mean
3.469
.010
.000
27.215
.178
.167
.034
.173
14.665
1.594
.945
2.034
.017
.055
.005
.035
.368
.003
.018
.009
.003
.000
.000
.000
.000
.000
.000
.008
.000
.000
.000
.451
.000
.000
.000
.000
.001
.000
.000
.000
.000
.192
.028
.318
.000
.000
.163
44.716
SD
.403
.011
Mean
Percent
.000
31.059
.252
.221
.054
.209
15.055
2.003
1.079
3.570
.018
.070
.005
.042
.452
.004
.020
.013
.008
.001
.000
.001
.000
.002
.000
.012
.000
.002
.005
.743
.002
.002
.000
.002
.005
.004
.052
.031
.000
.485
.303
.440
.050
.000
.255
52.012
N
3
3
Mean
Unc.
.070
3.177
.110
.032
.009
.047
1.717
.156
.084
.407
.002
.004
.001
.003
.025
.002
.002
.001
.001
.001
.000
.026
.001
.001
.001
.001
.001
.003
.005
.293
.004
.005
.006
.006
.008
.014
.059
.048
.001
.027
.280
.165
.038
.070
.026
5.320



SD
.000
3.391
.067
.050
.024
.035
.451
.429
.116
2.530
.001
.013
.000
.008
.112
.001
.002
.005
.005
.001
.000
.002
.000
.002
.000
.004
.000
.002
.004
.388
.003
.004
000
.004
.005
.005
.049
.035
.000
.355
.290
.131
.044
.000
.113
6.370



N
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3



Mean
Mg/m3
.000
500.204
4.099
3.514
.845
3.396
242.108
32.670
17.399
56.670
.283
1.104
.082
.668
7.147
.063
.319
.207
.125
.009
.002
.023
.007
.038
.000
.187
.000
.032
.072
11.766
.029
.045
.000
.035
.082
.074
.896
.449
.000
7.566
4.651
7.115
.753
.000
4.233
840.296



Mean
Unc.
1.156
71.253
1.827
.611
.172
.834
36.588
4.123
2.194
8.562
.041
.129
.023
.079
.814
.035
.042
.028
.022
.021
.008
.411
.010
.013
.017
.029
.023
.042
.078
5.025
.060
.078
.103
.106
.131
.233
.976
.802
.022
.862
4.661
2.815
.715
1.156
.603
119.700



SD
.000
84.244
1.444
.579
.283
.911
26.346
10.620
3.100
38.779
.030
.094
.003
.148
1.054
.008
.011
.062
.068
.016
.003
.038
.007
.034
.000
.071
.000
.029
.064
5.817
.050
.078
.000
.060
.068
.075
.889
.505
.001
4.861
4.508
2.287
.653
.000
2.390
172.625



N
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3



                                        262
-------
Analysis Summary, 298/01, Recovery Furnace, Particle Size: F
Element
F
NA
MG
AL
SI
P
S
CL
K
CA
TI
V
CR
MN
FE
CO
NI
CU
ZN
GA
GE
AS
SE
BR
RB
SR
Y
ZR
MO
TC
PD
AG
CD
IN
SN
SB
BA
LA
HG
PB
OC
EC
NO3
NH4
PO4
SO4

V/NI
BR/PB
Maximum Minimum
Percent Percent
.000
33.200
.003
.176
.047
.000
21.001
4.091
2.693
.205
.010
.005
.004
.006
.195
.003
.008
.009
.078
.001
.001
.005
.000
.052
.006
.000
.002
.002
.016
2.676
.010
.000
.006
.010
.011
.014
.000
.035
.000
.000
2.520
.156
.000
1.662
.000
60.908
Mean
.881
135.600
.000
31.675
.000
.056
.000
.000
17.310
3.766
2.516
.041
.003
.000
.003
.005
.076
.001
.002
.004
.012
.000
.000
.001
.000
.029
.002
.000
.001
.000
.006
1.152
.000
.000
.000
.000
.000
.000
.000
.000
.000
.000
1.076
.000
.000
.000
.000
55.274
SD
1.138
.000
Mean
Percent
.000
32.462
.001
.113
.016
.000
19.653
3.957
2.623
.125
.006
.003
.003
.005
.122
.002
.005
.006
.037
.000
.000
.003
.000
.037
.004
.000
.001
.001
.010
1.919
.006
.000
.002
.003
.005
.005
.000
.020
.000
.000
1.842
.078
.000
.554
.000
58.499
N
3
1
Mean
Unc.
.112
3.326
.057
.020
.012
.014
2.245
.310
.206
.019
.001
.001
.001
.001
.008
.001
.001
.001
.003
.000
.001
.001
.001
.002
.002
.001
.002
.004
.007
.495
.005
.006
.009
.009
.012
.020
.084
.071
.002
.003
.493
.192
.112
.126
.112
5.994



SD
.000
.764
.002
.060
.027
.000
2.037
.170
.094
.082
.004
.002
.000
.001
.065
.001
.003
.002
.036
.000
.001
.002
.000
.013
.002
.000
.001
.001
.005
.762
.005
.000
.003
.006
.005
.008
.000
.018
.000
.000
.726
.078
.000
.960
.000
2.904



N
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3



Mean
Mg/m3
.000
135.259
.003
.524
.088
.000
79.657
16.548
10.800
.560
.027
.011
.014
.021
.556
.008
.024
.026
.181
.001
.002
.013
.000
.164
.015
.000
.005
.003
.036
7.528
.018
.000
.005
.013
.024
.013
.000
.082
.000
.001
7.177
.351
.000
1.571
.000
242.016



Mean
Unc.
.433
19.257
.255
.103
.049
.056
12.031
2.086
1.362
.100
.006
.004
.004
.005
.065
.005
.005
.005
.022
.002
.002
.003
.003
.019
.006
.006
.006
.014
.026
2.061
.019
.025
.033
.036
.045
.079
.327
.276
.006
.013
2.037
.773
.433
.535
.433
34.456



SD
.000
48.857
.005
.424
.152
.000
19.070
6.201
3.311
.525
.025
.010
.004
.007
.472
.003
.018
.019
.224
.002
.003
.014
.000
.113
.007
.000
.004
.004
.007
2.730
.016
.000
.009
.022
.032
.022
.000
.075
.000
.001
2.467
.318
.000
2.720
.000
82.972



N
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3



                                        263
-------
Appendix D-5.  Area Source Emission Calculations
An area source emission inventory was performed for the Tideflats industrial area. The spatial
resolution of the grids was defined by the Universal Transverse Mercator (UTM) System at one
km2.  The inventory was performed using 1986 emission data.

Residential Heating

Emissions from residential heating are a function  of the population  density.   Therefore, a
detailed, block-by-block analysis was made for the Tacoma Tideflats area using the latest census
data (1980). The UTM grid network was overlaid on census maps and the population residing
on each block within a grid was totaled.  Population growth during the succeeding six years was
accounted for using citywide growth factors.

Distillate  oil:  Data on sales of distillate oil were obtained from major fuel oil distributors on
a countywide basis.  Known usage by all point sources was subtracted and the remaining fuel
was apportioned to each grid by population.  Variations between city and county in the number
of homes  using oil heat and the number of people per home were accounted for using census
data. The correction factor for the Tideflats is as follows:


(5.906 peopleV.021 oilV(2.21 people/home^          = .00144.
(530,800 people/county)(.187 oil)/(2.54 people/home)


PM10 emissions were calculated using these data and an emission factor from Compilation of Air
Pollution  Emission Factors (AP-42, 1985 Vol. I, pg.  1.3-2 8/82).  Assuming a PM10  fraction
of 50 percent (AP-42,  Vol. I, pg. 1.3-6, 10/86) and a population density of 1,000 people per
square kilometer, this would amount to:

(l.OQQ people/kmV82.000  x IP3 gal/yeart(2.2 lb/103 galV.50^.00144^ =  .011 ton/year.
                                    (5,906 people) (2,000 Ib/ton)

Even though the emission factor  is relatively high, the total emissions are negligible.

Residential wood combustion:  Data on sales of wood for residential use are not available.
Therefore, alternate schemes were employed to estimate PM10 emissions from residential wood
combustion.  One such scheme,  employed by the Oregon State Department of Environmental
Quality, is contained in the 1985 Portland Area Wood Heating Survey.   A total of 2,841
questionnaires were  randomly mailed to homes in the Portland area.  From the 974 valid
responses, 64 percent of the  wood burned was determined to  be used in wood stoves or
fireplace inserts and 36 percent in fireplaces without inserts. Homes that burned wood for heat
accounted for only 7.5 percent of the total number of homes, and used an average of 2.0 cords
of wood per year. A total of 58 percent of homes  used wood either for pleasure or for heat,
using an average of 1.3 cords per year.  The average usage for all homes was found to be 0.71
cords per year.  Emission factors for wood stoves/fireplace inserts and fireplaces were taken
from AP-42 (Vol. I, pg. 1.9-3, 5/83).  A PM10 fraction of 100 percent was assumed. From the
above information the  following  emission factor can be calculated:


EF  = (.64)(42 Ib PM10/ton wood)+(.36)(28 Ib PM10/ton)(5,251/4,635)  =  37 Ib PM10/ton
wood.
                                         265
-------
The average number of people per home in the City of Tacoma was taken from the Office of
Financial Management's 1986 Population Trends for Washington State.  In Tacoma, a grid with
1,000 residents would  contain 427 homes.  To adjust for the colder climate in Tacoma than
Portland, the ratio of the climatological average of heating degree days per year (5,251/4,635)
was  also factored into the calculation.  Assuming a cord  of wood  weighs  1.75  tons, the
emissions would be:

(.71  cord/home)(427 homes¥1.75 ton/cord^(37 Ib PM10/ton^(5.251/4.635)  =11.1 ton/yr.
                                        2,000 Ib/ton

To define a reasonable daily emission rate for residential heating, the ratio of heating degree
days on a typical December day to the total number of annual heating  degree days (30/4,539)
was  factored into the analysis.  For the woodsmoke case mentioned above:

(11.1 ton/year)(30/4,539)(2,0001b/ton)(.454 kg/lb) = 67 kg/day per thousand  residents.


Railroads

Data on distillate fuel (diesel) usage by switchyard locomotives were obtained from Burlington
Northern and Union Pacific.  PM10 emissions were calculated using these data and an emission
factor from (AP-42, Vol. H, pg. II-2-1, 4/73), assuming a PM10 fraction of 80 percent.  In the
Tideflats, all of the emissions were assumed to be located within a single grid.  The calculation
used for the Tideflats is as follows:


(600 x 103 gal/yrX2S lb/103 gal)(.8Q Ib PM^/lb TSP)  = 6.00 ton/year.
                                     2,000 Ib/ton


 5M
Data on ship activity were obtained from the Port of Tacoma.  A representative of the Port of
Tacoma reported  the total ship activity within the Port and the four  terminals which had
received the most use.

Ships in port use an average of 660 gallons of diesel fuel per day in diesel-powered generators
for lighting, heating, refrigeration, pumps, etc.  Representatives from the Port of Tacoma
estimated that the average time spent in port by a ship was between one and two days.  Using
an approximate emission factor from AP-42 (Vol. II, pg. II-3-2, 1/75) and a PM10 fraction of
50 percent  (AP-42, Vol.  I, pg. 1.3-6, 10/86)  and  assuming a 24-hour turnaround time, an
example emission can be calculated to  be:


(439 ships/yr)f24 hr/ship)(1.04 lb/hr)(.5Q Ib PM^/lb TSP) =  2.74 ton/year.
                                     2,000 Ib/ton


Motor Vehicles

The calculation of exhaust emissions from motor vehicles is a long and tedious process.  The
calculation includes a very slight dependence on the vehicle speed and a strong dependence on
the vehicle mix.  The emission factors for light-duty cars and trucks are both around .05  grams
per vehicle  mile traveled (g/VMT). Heavy-duty gasoline vehicles emit roughly three times as
much as light-duty vehicles;  however, the majority of the  total emissions come from heavy-

                                          266
-------
duty diesel trucks.  Even though they constitute only about 10 percent of the vehicles on the
road in these areas, they emit nearly 75 percent of the paniculate matter. The emission factor
for these vehicles is 1.85 g/VMT,  37 times higher than for light-duty vehicles.

The plan used to compute motor vehicle emissions per grid in the Tacoma Tideflats  area
involved defining three speed zones (10, 35, and 55 mph), each with its own vehicle mix.  The
20-mph zone was chosen to represent downtown and residential traffic (collector streets), and
the average vehicle mix that was used was provided by the Washington State Department of
Transportation (DOT). The 35-mph zone was chosen to represent  the major arterial streets,
which, in these areas, have roughly four times as  many heavy-duty  diesel trucks and twice as
many heavy-duty gasoline trucks.   The 55-mph zone was chosen to represent highways and
freeways, and contained the standard DOT mix.   The mix of vehicles in each of these zones
is shown in Table 1:
Table 1.  Vehicle Type Mix
Type
Description
55 mph
20 mph
35 mph
LDGV       Light-Duty Gasoline Vehicle
LDGT1      Light-Duty Gasoline Truck (GVW <  6,000 Ib)
LDGT2      Light-Duty Gasoline Truck (GVW 6,001-8,500 Ib)
HDGV       Heavy-Duty Gasoline Vehicle (GVW  > 8,500 Ib)
LDDV       Light-Duty Diesel Vehicle (GVW  < 8,500 Ib)
LDDT       Light-Duty Diesel Truck (GVW < 8,500 Ib)
HDDV       Heavy-Duty Diesel Vehicle (GVW >  8,500 Ib)
MC         Motorcycle

             Total
                                                    1.000
              .588
              .077
              .046
              .084
              .057
              .007
              .132
              .009

              1.000
A stop-and-go driving pattern was used to model emissions in the 20-mph and 35-mph zones,
while a steady cruise was used for the 55-mph zones. Tampering was accounted for assuming
1.7 percent catalyst removal and 9 percent misfueling (AP-42, Vol. II, pp. L 2-44 and L 2-
50).

The procedure used to calculate emission factors is contained in AP-42 (Vol. H, Appendix L,
9/85). It considers emissions of lead,  sulfate, and carbon from vehicles of one to 20 years in
age for each of six vehicle classes.  The vehicle mix is  weighted by the annual mileage
accumulation rate for each model year. The  registration mix is shown  in Table 2:
                                         267
-------
Table 2. Vehicle Registration Age Mix
                LDDV         LDDT          HDGV
  Year          LDGV        LDGT1         LDGT2         HDDV           MC
      1            .045           .062            .037            .078           .167
      2            .072           .096            .070            .136           .159
      3            .090           .095            .078            .135           .134
      4            .089           .104            .086            .132           .142
      5            .087           .084            .075            .100           .131
      6            .084           .077            .075            .091           .080
      7            .080           .077            .075            .083           .051
      8            .076           .064            .068            .063           .028
      9            .070           .054            .059            .045           .010
     10            .062           .043            .053            .033           .098
     11            .053           .036            .044            .025           .000
     12            .046           .024            .032            .015           .000
     13            .039           .030            .038            .013           .000
     14            .032           .028            .036            .011           .000
     15            .025           .026            .034            .010           .000
     16            .018           .024            .032            .008           .000
     17            .012           .022            .030            .007           .000
     18            .008           .020            .028            .006           .000
     19            .006           .018            .026            .005           .000
     20            .006           .016            .024            .004           .000

  Total           1.000          1.000           1.000           1.000          1.000
The resultant emission factors  (including brake and tire wear) for the 20-, 35-,  and 55-mph
zones, were .12, .31, and .12 g/VMT, respectively.

The next step was to calculate the VMT within each grid for each speed category.  Traffic
count data were acquired from the Traffic Engineering Divisions of the city of Tacoma. These
numbers, when multiplied by the appropriate length of roadway,  give the VMT.  The product
of the VMT per grid and the appropriate emission factors gives the total emissions per grid.

Resuspended Road Dust

The emission factor for road dust is a function of the vehicle speed. High-speed roadways are
swept clean by the turbulence induced by the flow of traffic. For principal and  minor arterials
(35 and 25-mph zones), the factor used was 2.8 g/VMT.  For limited-access  highways (55-
mph zones), the factor used was 0.3 g/VMT (AP-42, Vol.  I, pg. 11.2.5-5, 9/85). For a grid
having arterial streets with 10,000 VMT per day, the resulting emissions would be:

(10.000 VMT/dayK2.8 g/VMW365 day/yearl  =11.3 ton/year PM10.
       (454 g/lb)(2,000 Ib/ton)
                                         268
-------
Conclusions

The results of the inventories clearly show the importance of resuspended road dust and motor
vehicle exhaust.  Ambient impacts from woodsmoke are also important. The emissions from
the use of natural gas and distillate  oil for residential heating are negligible.  Table  3
summarizes the results of the PM10 area source inventory for the base year 1986:


Table 3.  PM1B Area Source Inventory-1986	

	Source	Tideflats	

                                     Tons/year       kg/day

                    Exhaust                 58          143
                    Road Dust             357          887
                    Ships                    9           22
                    Railroads                 6           15
                    Airplanes                —           —(a)
                    Woodstoves           	18.          109

                    Total                  448        1,176


(a) Insignificant

For the 1991 baseline inventory the following growth factors were assumed:


Growth Factors 1986-1991	

	Source	Tideflats	

                    Exhaust                   + 3% per  year
                    Road Dust                + 3% per  year
                    Ships                         no change
                    Railroads                      no change
                    Airplanes                            N/A
                    Woodstoves                   no change
Growth factors for vehicular sources (i.e., exhaust and road dust) were determined by the
Tacoma traffic engineering division based on the rate of growth in traffic volumes over the
years 1984-1986. Growth factors for residential heating (i.e., wood stoves) were based on the
rate of population growth over the years 1980-1986 (see Residential Heating).
                                         269
-------
APPENDIX E.  LABORATORY RESULTS--
18-DAY RECEPTOR MODELING FIELD STUDY
     E-l. Ambient Monitoring for Receptor Modeling Study  	273
     E-2. Fine-Particle Results  	279
     E-3. Coarse-Particle Results	291
     E-4. VOC Results	301
     E-5. Meteorological Data	313
     E-6. Linear Correlations Between Sites  	315
     E-7. PAH Results	323
                               271
-------
Appendix E-l. Ambient Monitoring for Receptor Modeling Study	


FIELD SAMPLING

Dichotomous PM10 Filter Samples and Sampling Devices

AREAL arranged for its on-site contractor, NSI Environmental Services, to make all particle
sampling media available to NBA [gravimetric determinations were made on 75 pairs (coarse
and fine) of 37-mm-diameter ringed Teflon filters; 72 pairs of filters for field sampling, and
three pairs for field blanks].   Additionally, 80 pairs of 37-mm-diameter quartz filters were
obtained by the on-site contractor from Sunset Laboratories;  the quartz filters were certified as
clean, pre-fired,  and placed in aluminum-foil-lined plastic Petri dishes.   For field sampling
purposes,  80 pairs of quartz filters were used, with eight pairs set aside as field blanks.  For
both sets of quartz and Teflon filters, field data sheets with information on filter number, flow
rate, sampling time and dates, and sample location were also supplied.  AREAL specified that
for the receptor modeling  work,  sampling periods  would consist  of 12-hour  intervals;
specifically, 7:00 a.m. to 7:00 p.m. and 7:00 p.m. to 7:00 a.m. cycles.  AREAL also provided
the standard operating procedures for the dichotomous samplers.

At each site, two  dichotomous samplers were  used for the quartz and Teflon filters.  The
following Sierra-Andersen equipment was used: Series 240 virtual impactors; Model 246B PM10
inlets (flat top design);  and virtual impactor filter holders.  The  samplers and inlets were
obtained from EPA Region 10, Oregon Department of Ecology, and NEA; obtaining equipment
that met current  reference method specifications necessitated using these multiple sources.

Prior to field operations, NEA was responsible for training monitoring personnel and calibrating
the sampling devices.  During the sampling program, NEA conducted flow checks, performed
sampler maintenance, completed field data forms, made filter changes, and refrigerated exposed
filters.  NEA  sent the filters back to AREAL in two shipments, corresponding to the two
sampling phases.

The dichotomous  pump  units were calibrated by  NEA technicians at  the home office  in
Beaverton, Oregon.  Flows were then converted to  the seasonal average temperature and
pressure in Tacoma.  Also, the NEA inlets were carefully cleaned and inspected for damage
before being sent to the field.  Dichotomous tubing was examined for cracks and bends, and
technicians installed new fittings on the tubing.

The PM10 samplers ran concurrently with the VOC canister samplers (VOCCS) during the 12-
hour intervals  described earlier.  Technicians changed filters and canisters every 12 hours and
recorded data  on field  sheets.   Information on the  field data sheets included  sampling data,
sampler and canister identification,  site location,  sampling  time, flow checks, and gauge
pressure.  Particulate samples were removed immediately and placed in the Petri dishes with
the corresponding identification numbers. Canisters were shut off and sealed with a swage-lock
cap fitting to  prevent leakage, returned to their respective shipping boxes, and shipped to
Battelle-Columbus for laboratory analysis. The original field data sheets,  which included field
data such as barometric pressure,  temperature,  and  sky conditions, were included in the
shipping box.  The dichotomous filters were placed in Petri  dishes and these were wrapped in
aluminum foil to preserve the sample.

VOC Canisters  and Sampling

A single VOCCS was located at  each site.   At the Morse Industrial  site, an EPA-modified
Wedding VOCCS sampler was installed.  The modification was made by removing  the critical


                                         273
-------
orifice and replacing it with a mass-flow controller; this enabled the sampler to operate at a
variable flow rate and collect a larger volume of air.  An Andersen VOCCS system was used
at the Alexander Avenue site; like the  modified Wedding unit,  the Andersen system  also
operates by way of a mass flow  controller.  Certified-clean, evacuated,  stainless steel VOC
canisters were provided by Battelle-Columbus under a separate contract.  In addition to the 72
canisters used for the field sampling, two field blank canisters were also submitted for analysis.

ANALYTICAL MEASUREMENTS

Gravimetric Measurements

Polyolefin-ringed Teflon filters were used  for coarse and fine particle mass determinations.
Individual  filters were placed in  plastic  Petri dishes with covers that were prelabeled with
identification numbers (199101C to 199175C for coarse filters and 299101F to 299175F for fine
filters).  Gravimetric measurements were performed on a Metier ME22 microbalance with a
Metier BA25 digital display and Metier BE22 balance control unit. The microbalance was kept
in a temperature- and relative-humidity-controlled room (nominally 50 percent relative humidity
and 72 °F). For both tare and final gravimetric measurements, the filters were  allowed to sit
overnight in the balance room to  equilibrate.

Each weighing session began and ended with a calibration check using Class S weights.  Repeat
measurements were performed on every sixth filter. The mass loadings were calculated as the
difference  between the final mass and the tare mass.  In cases where replicate measurements
were made, the average value of  the two readings was used for subsequent calculations.

Quartz Filter Procedures

Prepared quartz filters were purchased directly from Sunset Laboratories. These filters arrived
individually wrapped in plastic Petri  dishes lined with aluminum foil.  Unique identification
numbers were affixed to the dishes (identification numbers 199201 - 199280 for coarse particle
sampling and 299201 to 299280 for fine  particle  sampling).  After the  filters were numbered
they  were given to EPA  to be sent to NEA Laboratories for sampling.   Data forms to be
completed in the field were also sent to NEA. The samples were returned in two lots together
with  the Teflon filters (December sampling and  January sampling) and stored temporarily in a
laboratory refrigerator.

The quartz filters from the fine-particle sampling were apportioned for three separate analyses:
elemental/organic carbon analysis, ion chromatography analysis, and PAH analysis.  One-half
of a  filter was to be supplied for the first  analysis and one-quarter of a filter for each of the
other two  analyses.  Filters were first cut into halves by carefully visually bisecting the  filter
deposit area and then  cutting with  a clean  razor blade.    One of the  filter halves was then
further cut into two parts, again being careful to split the deposit area.  As a check, each  filter
fraction was weighed;  however, it was found that the nonuniformity of the quartz filters and
the asymmetrical deposits made these measurements unusable.

The filter halves were  returned to the labeled Petri dishes and sent to Sunset Laboratories for
elemental/organic carbon analysis.  One  of the  filter quarters was placed in a pre-cleaned 30
mL polyethylene bottle for ion chromatography analysis.  The second  filter quarter was placed
in a new Petri dish that was labeled with the same identification number as the original whole
filter.

No analysis was planned for the  quartz filters containing the coarse-particle fraction so  these
filters were stored in a freezer  until completion of the project.
                                          274
-------
Ion Chromatography Analysis

Ion chromatography analysis was performed on the 80 quartz filter quarters that resulted from
the filter cutting operations described earlier.  Seventy-two of the fractions were cut from field-
sampled filters and eight of the fractions were cut from the field blanks.

Filter extraction bottles (30-mL polypropylene bottles) were carefully cleaned prior to use.
Each bottle was rinsed first with deionized water and then filled with ion chromatography eluent
and sonicated for 30  minutes.  The bottles were then emptied,  dried in a vacuum  oven, and
capped.  Bottles were labeled with filter identification numbers. These were loaded with the
filter quarters during  the filter quartering operations  described earlier.   After loading, the
sample bottles were delivered to the analytical laboratory and refrigerated until extraction.

Ion chromatography analysis  was performed with a Dionex Model 10 instrument.  A Dionex
AG3  guard column and an AS3 separatory column were used in conjunction with a fiber
suppressor column and a conductivity detector.  The ion chromatography eluent composition
was 0.0024M sodium carbonate and 0.0018M sodium bicarbonate.  Data were recorded with
a SpectraPhysics Winners system for data storage.

Sets of sample bottles were grouped together to  make up a sufficient group for one day of
analysis.  For the filter extraction,  15.0 mL of the ion chromatography eluent were added to
each bottle.  The bottles were sonicated for 30 minutes in an ultrasonic bath and then  stored
overnight in a refrigerator for analysis the next day.  An extracting solution blank sample was
included with each set of filters for analysis.  The extracting solution blank was prepared by
placing ion chromatography  eluent in a cleaned  empty bottle  and  then sending this  sample
through the same sonication and storage procedures as the regular filter samples.  Each sample
was filtered with an iso-filter prior to loading it in an ion chromatography  sample cup.  This
prevented problems that arise from quartz fibers that remain suspended in the eluent after the
filters break up after  sonication.

A quality control solution containing nitrate and sulfate of known concentrations was prepared.
A sample of this solution was run during the ion chromatography analysis as the second sample
of a run sequence and approximately every sixth sample position after that.  The results from
these repeat measurements were used to calculate the daily relative standard deviation for each
component.

Organic Carbon and Elemental Carbon Analysis

Quartz   fine-fraction   filter   halves  were   mailed  to  Sunset  Laboratories   for  organic
carbon/elemental carbon analysis by a thermal-optical method similar to that of Johnson et al.
(1981).  These filters were mailed in their original foil-lined Petri dishes and labeled with the
unique identification numbers for the study.

Results were supplied from Sunset Laboratories both as hard copy and as LOTUS and  ASCII
floppy disk files.   Data were presented as jig carbon per  cm2 for both the organic carbon
determination and  the elemental carbon determination.  Error bars were  reported for each
sample for each of the determinations.

X-ray Fluorescence Analysis

Energy-dispersive XRF was used to determine elemental composition of the Teflon filter aerosol
deposits (Dzubay et al., 1982). In this method,  the sample is irradiated with  x-rays, which
ionize the constituent  atoms by removing the inner electrons. The resulting excited state atom
relaxes back to the ground state by emission of photons whose energies are characteristic of the
atom.  The emitted photons are detected by a solid state detector which registers  each detection

                                          275
-------
event as a voltage pulse proportional to photon energy.  Thus, by measuring the voltage pulses
and amplitudes, the species that are present can be quantified. The spectrometer used in this
study is located at EPA in Research Triangle Park, North Carolina.   It was constructed by
Lawrence Berkeley Laboratory in Berkeley, California.

The spectrometer is calibrated using commercially available metal foils and salts (Micro-Matter
Co.,  Eastsound,  Washington),  which have  been  evaporated  onto  thin  membranes  and
gravimetrically assayed to determine concentration.  Polymer films containing organo-metallic
compounds are also used for calibration.  A sensitivity curve for all of the elements associated
with each fluorescer is determined by least squares fitting.  This provides an accurate sensitivity
for elements for which accurate calibration standards may not be available.

Background spectra from blank filters are measured for all types of filters and their lot numbers
currently in use. Approximately 36 blanks are measured for background determination. If any
contamination is found on a blank,  its  spectra is not used in background determination.  The
spectra from the acceptable blanks are  stored  on file for use in spectral processing of samples
on filters of the same type and lot number. Elemental shape spectra are also used in spectral
processing.   These  spectra are measured from clean standards which may be calibration
standards and are stored for least squares fitting of sample spectra.  Data analysis is performed
by least  squares fitting.  The elemental  shapes and  the background spectra are fitted to the
unknown spectra.  The data are then corrected for  x-ray attenuation and spectral overlap.

In total,  72 pairs of filters and three pairs of unsampled  field blanks were analyzed.  Filters
were loaded in sample trays and automatically processed through the system in a series of three
analysis  runs.  Before and  after  each  run, six quality control  standards were automatically
analyzed  as a part of the run. to validate the data.  The results  of two  standard  reference
material  samples were  reported with every run.  Reported uncertainties represent one standard
deviation.

Due  to  a  computer  programming  error  discovered in early 1991,  the attentuation
corrections for dichot coarse Mn, Fe,  Co,  Ni, Cu, and Zn were not calculated into the
coarse-particle data as reported from  the laboratory.  The  reported values are low by
approximately 5% for Fe, 7% for Co, Ni, Cu, and Zn, and less than 6% for Mn. Because
the corrections would be approximate and less that one standard deviation, the  data have
not been corrected for this error.

PAH Analysis

The quartz  filter  quarters designated for PAH analysis were grouped  into  seven sets.   The
samples  were grouped as listed below:

       Set 1   Morse Supply site,  December, boiler running;
       Set 2   Morse Supply site,  December, boiler not running;
       Set 3 - Morse Supply site,  January, boiler running;
       Set 4   Alexander Avenue site, December, boiler running;
       Set 5 - Alexander Avenue site, December, boiler not running;
       Set 6 - Alexander Avenue site, January, boiler running; and
       Set 7   Eight unsampled filters (field blanks).

The "boiler" referred to above was the Simpson Tacoma Kraft  facility recovery boilers and
hogged fuel boilers.

The filters for each  set were added to 250-mL  round-bottom flasks and connected to reflux
condensers for extraction. Approximately 175 mL of methylene chloride was used  during the
20-hour extraction period.  After extraction, each flask was reduced to several mL on a rotary

                                          276
-------
evaporator.   The contents were carefully transferred to volumetric centrifuge tubes with
additional washings  of the round bottom flasks with methylene chloride.  The samples were
reduced in volume to less than one mL and transferred to 1-mL volumetric flasks.  The samples
were then diluted up to 1-mL.

It would have been desirable to perform gravimetric analyses on aliquots of the fractions.
However, the total mass was insufficient to make these measurements and still ensure that there
would  be adequate  sample remaining for the organic analyses.   The seven samples  were
delivered to the GC/MS  laboratory  and FTIR for analysis.

Preliminary analysis of  the 1-mL  extracts showed that they were too dilute, so they were
concentrated down to  100 /xmL under streams  of nitrogen. Five samples (sets 1, 2, 4, 5, and
7) were analyzed by full scan GC/MS using an Hewlett Packard 5970 MSD.  All seven samples
were analyzed by selected  ion monitoring (SIM) for detection of PAHs and retene.

VOC Analysis

A cryogenic gas chromatographic system was used to analyze the VOC canister samples.  This
system was composed of two components;  a collection apparatus and  an analysis apparatus.

Sample collection was accomplished with a modified Nutech Model 320-01 cryogenic unit. The
Nutech instrument contained two subsystems.  An electronics console was employed for setting
and controlling various temperature zones, while the sample handling unit contained the six-
port valve and cryogenic trapping components. Three  temperature zones were controlled by
the console. The valve and transfer lines were maintained at 120°C. During sample collection,
the trap temperature was regulated by the electronics console, which controls the release of
liquid nitrogen via a solenoid valve. During the current study, the temperature setpoint of the
trap during sample collection was -160 +. 5°C.  A cylindrically coiled 250-watt heater was used
to heat the trap during the sample desorption cycle. The  trap was wrapped around the  heater
to promote heat transfer during the desorption cycle (-160 to  120°C in 60 seconds).   Rapid
heating  of the trap provided efficient  transfer of  sample components  onto the  gas
chromatographic column.  The sample trap was constructed of 20- x 0.2-cm-ID stainless steel
tubing packed with  silanized glass  beads (60/80 mesh).  A Carle six-port air-actuated valve
(Hach  Company) was used to facilitate sample collection and injection.

A Perma Pure dryer (Model MD-125-48F) with a tubular hygroscopic  ion-exchange membrane
(Nafion) was used to remove water vapor selectively from the sampled gas stream.  The dryer
was purchased in a shell and tube configuration. The tube size had a 30- x 0.1-cm ID and was
imbedded within a shell of Teflon tubing of 0.25-cm ID. Sample flow through the tube was
maintained at 35 mL/min with a mass flow controller (Tylan FC-260). A countercurrent flow
of dry  zero air (200  mL/min) was used to purge the  shell.  Use of the dryer permitted collection
of larger volumes of sample air (350 mL), thereby lowering the limit of detection.

Sample analysis was achieved  with a Hewlett Packard Model 5880A gas  chromatograph
equipped with a flame ionization and mass selective  detection system (HP 5970).  A 50- x 0.32-
mm-ID, OV-1 fused silica column (Hewlett Packard) was used to resolve the target compounds.
The column flow was  maintained at 3 mL/min with a mass flow controller.  Zero grade helium
(Matheson) served as the carrier gas. Optimum analytical results were achieved by temperature
programming the gas  chromatographic column from -50° to 150°C at 8°C/min. The column
exit flow was split  using a low dead-volume tee (Alltech, Inc.).  One-third of the flow was
directed to the mass selective detector; the remaining flow passed through the flame ionization
detector.

The mass selective  detector was operated in  the SIM mode of operation for VOC canister
analyses.  In this mode, the mass  spectrometer monitored only preselected ions, rather than

                                         277
-------
scanning all masses continuously between two mass limits.  As a result, increased sensitivity
and improved quantitative analysis were achieved.  For the canister samples, two characteristic
ions were monitored for each target compound, and quantification was based on peak areas.
Details of these analyses can be found in Pollack and Smith (1990).
                                         278
-------
Appendix E-2. Fine-Particle Results
                                         279
-------
Site

PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
PSAPCA
Date

05-Dec-89
05 -Dec -89
06-Dec-89
06-Dec-89
07-Dec-89
07-Dec-89
08-Dec-89
08-Dec-89
09-Dec-89
09-Dec-89
10-Dec-89
10-Dec-89
11-Dec-89
11-Dec-89
12-Dec-89
12-Dec-89
13-Dec-89
13-Dec-89
H-Oec-89
H-Dec-89
15-Dec-89
15-Dec-89
02-Jan-90
02-Jan-90
03-Jan-90
03-Jan-90
04-Jan-90
04-Jan-90
05-Jan-90
05-Jan-90
06-Jan-90
06-Jan-90
07-Jan-90
07-Jan-90
08-Jan-90
08-Jan-90
Teflon
Start- Duration
Time
725
1800
630
1851
643
1847
641
1842
636
1855
650
1840
652
1845
710
1840
641
1845
646
1838
645
1840
705
1919
714
1915
711
1912
700
1845

1845
645
1830
640
1845
(min)
685.0
705.3
725.0
707.0
724.2
705.8
716.9
710.5
733.4
713.7
705.4
727.5
705.3
740.0
682.4
711.1
723.9
710.3
709.8
719.9
711.8
722.5
716.7
709.9
719.5
712.8
724.4
701.5
696.9
758.2
690.0
704.6
724.4
702.4
730.8
703.0
Fine Organic Elemental
Mass Carbon Carbon
1C
N03-
1C
S04--
ug/m**3 ug/m**3 ug/m**3 ug/m**3 ug/m**3
20.79
19.90
12.11
22.87
37.12
9.90
7.15
5.06
8.98
42.98
21.13
52.31
64.43
60.15
48.85
24.79
29.41
38.97
36.93
41.87
27.67
15.65
15.88
14.15
7.31
7.65
7.25
14.99
10.92
4.35

2.17
6.15
4.26
10.29
10.51
13.70
6.88
2.26
10.26
13.14
3.43
2.62
1.65
3.27
19.97
8.46
14.96
21.06
29.81
18.79
9.27
11.72
13.32
14.32
18.04
9.74
2.41
7.48
5.66
3.55
4.11
3.21
6.20
5.15
1.97
4.93
1.25
1.70
2.22
4.54
4.98
5.02
1.61
0.48
1.18
3.05
0.61
1.14
0.27
0.59
1.76
0.75
1.22
3.54
2.71
3.10
1.60
3.49
2.88
3.02
2.97
2.44
0.47
2.70
0.82
1.73
0.87
1.53
0.89
2.94
0.53
1.18
-0.01
0.46
0.32
2.99
1.29
1.26
0.71
0.42
1.28
1.55
0.14
0.10
0.21
0.41
0.98
1.22
1.82
3.11
2.25
3.31
2.61
2.34
1.18
1.72
1.74
2.01
0.95
0.84
0.47
0.37
0.47
0.24
0.83
0.41
0.23
0.48
0.06
0.18
0.23
0.34
0.50
2.41
1.69
0.61
1.93
5.18
2.07
1.97
0.85
0.51
1.11
2.40
1.89
6.22
4.19
4.37
2.30
2.89
2.37
4.32
4.41
3.78
1.51
1.92
1.38
1.67
1.13
1.71
1.70
1.84
1.22
0.86
1.03
1.23
0.60
0.86
0.70
281
-------
PSAPCA
FINE FILTER
ERROR ERROR ERROR
SDATE STIHE GHAS GMAS AL AL SI SI S
S
ERROR ERROR
CL CL
NG/H3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/H3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
725
1800
630
1851
643
1847
641
1842
636
1855
650
1840
652
1845
710
1840
641
1845
646
1838
645
1840
705
1919
714
1915
711
1912
700
1845
0
1845
645
1830
640
1845
20790
19910
12110
22870
37130
9895
7145
5053
8986
42960
21140
52280
64460
60150
48880
24800
29410
38980
36920
41860
27660
15640
15870
14150
7300
7652
7168
14970
10920
4353
-4532
2171
6157
4265
10280
10510
1845
1793
1744
1788
1746
1791
1763
1778
1725
1771
1793
1736
1793
1708
1854
1778
1746
1780
1780
1756
1775
1748
1784
1780
1756
1773
1746
1801
1836
1688
1832
1793
1746
1801
1729
1798
53.43
8.04
17.52
5.98
125.6
107.1
-85.42
244.5
683.3
53.07
200.8
7868
242.5
107
386.9
652
282.1
1167
154.1
24.61
389.6
3.78
1.71
3651
-16.71
69.7
-28.51
188.7
38.27
335.6
37.16
113.9
103.6
35.37
29.71
33.11
39.39
39.74
34.17
38.15
46.72
39.22
38.04
50.54
109
39.51
48.41
1180
62.11
47.03
76.57
108.5
63.12
183.4
48.59
41.38
72.25
33.33
37.44
536.3
32.22
33.91
30.05
47.26
33.78
60
35.76
38.74
37.44
33.84
33.51
36.87
106.8
21.57
16.25
45.07
101.7
13.75
-9.407
5.033
51.27
23.27
3.869
92.79
92.45
51.54
126.8
71.93
98.95
80.92
123.8
59.24
156.8
44.79
69.21
79.7
4.016
-0.058
60.42
19.75
15.99
30.47
66.05
18.13
6.899
22.85
31.39
13.35
21.16
14.8
12.67
15.62
21.8
12.94
13.58
11.45
15.05
13.6
12.83
20.68
22.82
17.57
25.68
18.48
22.28
20.08
24.05
18.04
27.11
14.58
17.33
17.88
11.8
11.04
14.89
13.08
12.2
11.93
16.07
12.49
11.83
12.48
12.98
12.86
678.2
761.8
687.7
873.1
1730
864.8
704.4
295.7
165.1
525.9
996.1
850.9
2554
1692
1868
876.8
1125
1116
1766
1526
1484
1029
512.1
403.8
500.8
337.5
608.9
544.9
447.1
238.4
241.7
363.1
463.1
211.8
328.3
253.1
52.57
57.89
52.25
66.54
130.3
65.39
53.83
23.4
14.52
41.63
75.37
64.71
192.8
128.1
140.9
66.79
86.36
85.16
132.8
115.2
111.6
77.47
39.8
31.43
38.24
26.17
46.87
41.7
34.62
19.2
19.71
28.05
35.56
17.23
26.4
20.64
239.1
248.7
97.12
194.8
308.2
45.16
79.9
208
208.1
327.9
77.71
272.4
533.2
538.1
373.2
179.8
150.1
302.3
146.6
169.1
128.2
42.3
66.28
124.9
35.47
10.47
19.13
57.88
21.13
109.8
79.93
259.8
393.3
100.4
150.5
91.22
18.78
19.36
8.446
15.51
23.89
5.262
7.492
16.2
16.35
25.22
7.212
21.1
40.63
40.81
28.71
14.55
12.62
23.42
12.25
13.83
10.78
4.886
6.587
10.37
4.48
3.229
4.258
5.89
3.855
9.13
7.287
19.96
29.73
8.648
12.19
8.193
282
-------
PSAPCA
FINE FILTER
SDATE STIME K
ERROR ERROR
K CA CA
NG/M3 NG/M3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
725
1800
630
1851
643
1847
641
1842
636
1855
650
1840
652
1845
710
1840
641
1845
646
1838
645
1840
705
1919
714
1915
711
1912
700
1845
0
1845
645
1830
640
1845
113.7
133
86.02
128.4
223
54.9
23.71
24.15
59.96
289.5
112.2
186
237
380
223.1
148.3
139.1
208.7
145.6
170.8
120.3
153.8
64.1
62.23
25.16
33.87
29.11
126.9
50.59
20.93
121.3
21.26
33.73
70.08
82.95
85.81
9.003
10.39
6.972
10.05
16.89
4.912
3.288
3.005
5.279
21.74
8.833
14.18
17.94
28.41
16.93
11.47
10.85
15.84
11.28
13.1
9.419
11.8
5.627
5.391
3.191
3.598
3.266
9.881
4.655
2.853
9.529
2.985
3.588
5.936
6.771
7.026
81.34
22.1
41.23
30.48
65.47
45.3
23.72
13.08
21.11
17.44
23.57
43.1
79.21
30.42
89.62
47.12
102.7
40.42
63.47
29.77
75.6
17.53
42.32
29.32
22.74
12.32
28.79
74.46
26.09
11.48
38.54
12.85
21.06
17.45
35.06
17.64
6.841
3.801
4.222
3.929
5.853
4.54
3.734
2.952
3.814
3.188
3.444
4.486
6.803
3.856
7.606
4.781
8.376
4.421
5.743
3.882
6.449
3.055
4.491
3.751
3.361
2.975
3.526
6.337
3.533
2.764
4.25
3.104
3.584
3.34
3.928
3.331
ERROR
TI TI V
ERROR
V
NG/M3 NG/M3 NG/M3 NG/M3
5.869
-9.703
3.08
5.478
8.402
3.374
0.9957
0.436
8.546
3.801
-3.246
7.219
-4.232
5.031
9.649
8.016
-4.285
7.359
9.997
6.574
1.331
4.057
2.158
6.349
3.614
2.636
2.298
0.756
3.468
3.144
5.248
0.5937
•0.6227
-0.4937
5.969
0.787
9.932
4.676
3.919
4.162
4.677
4.01
5.118
4.115
5.17
3.79
4.616
3.891
5.645
5.34
4.523
5.512
5.728
4.178
5.195
5.098
4.417
3.849
4.309
4.39
4.123
5.289
3.739
4.027
4.215
4.386
4.235
4.748
5.178
4.132
3.799
5.986
5.432
1.379
6.091
9.196
25.35
8.704
5.253
5.852
3.24
4.364
8.746
9.459
11.98
8.105
14.62
7.067
1.98
6.872
20.06
9.232
7.613
7.665
5.39
4.846
10.84
16.75
11.67
6.743
8.839
3.351
3.433
7.606
8.554
3.943
4.823
3.485
3.369
2.145
1.582
2.003
4.274
1.763
4.161
3.097
4.417
1.945
1.9
1.905
5.736
5.342
2.817
2.028
4.905
2.249
2.714
4.736
2.066
1.612
1.686
3.182
1.878
2.484
2.446
1.736
1.78
1.573
1.569
1.843
5.657
2.478
1.49
2.073
ERROR
CR CR
NG/M3 NG/M3
1.104
3.05
3.91
0.7272
6.45
0.9116
0.6384
0.7314
1.339
1.093
1.255
9.194
7.139
2.908
3.709
3.735
3.942
1.44
4.025
1.637
3.443
0.487
1.463
3.526
0.58
0.388
3.192
1.566
1.196
0.7285
0.747
1.403
-0.3558
0.4011
1.065
0.1956
0.7008
0.8233
0.7762
0.6899
1.205
0.6454
1.064
0.8206
1.107
0.6762
0.6228
1.175
1.54
1.302
0.9226
0.7963
1.29
0.7596
0.8521
1.173
0.7866
0.5791
0.7056
0.9563
0.6276
0.6185
0.7953
0.6688
0.6303
0.5601
0.6228
0.6314
1.279
0.7526
0.6401
0.6236
                                                 283
-------
PSAPCA
FINE FILTER
ERROR ERROR ERROR ERROR ERROR
SDATE STIME MN HN FE FE NI NI CU CU ZN ZN
NG/M3 NG/H3 NG/H3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
725
1800
630
1851
643
1847
641
1842
636
1855
650
1840
652
1845
710
1840
641
1845
646
1838
645
1840
705
1919
714
1915
711
1912
700
1845
0
1845
645
1830
640
1845
34.16
16.04
15.22
19.88
31.84
6.654
8.947
2.25
10.66
26.93
7.817
13.31
56.06
37.46
46.25
27.55
38.96
35.76
58.5
38.42
31.37
11.97
23.51
4.942
5.11
1.508
8.271
8.495
14.48
1.568
10.62
1.344
2.323
3.358
23.04
9.534
2.825
1.659
1.527
1.825
2.708
0.9546
1.23
0.7027
1.261
2.298
0.9951
1.379
4.37
3.09
3.7
2.384
3.209
2.966
4.557
3.171
2.641
1.248
2.139
0.8728
0.8709
0.6956
1.031
1.047
1.451
0.6519
1.226
0.6787
0.7944
0.8128
2.028
1.173
194.7
69.56
158.5
104.2
343.8
31.32
60.39
15.76
40.56
50.65
21.99
86.75
420.1
130.6
267.1
142.8
248.5
138
377.2
125.9
231.9
47.03
217.7
58.16
37.94
12.75
66.41
57.61
111.9
12.62
122.7
6.715
5.242
13.22
337.5
47.19
18.93
7.451
15.51
10.55
32.75
3.976
6.622
2.573
4.811
5.642
3.173
8.914
39.87
12.95
25.67
14.12
23.91
13.68
35.87
12.56
22.35
5.263
21.08
6.334
4.515
2.42
7.029
6.289
11.27
2.301
12.25
2.09
1.871
2.542
32.14
5.38
NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3
0.6223
3.028
6.676
5.196
19.51
5.802
3.94
3.117
2.962
0.6771
6.633
30.75
14.89
4.501
8.645
6.155
7.559
7.02
14.11
6.306
7.386
4.388
2.263
1.709
1.55
7.741
7.116
4.488
0.9557
0.9987
0.0644
3.722
3.425
0.7153
4.233
-0.4277
0.9622
1.209
1.327
1.248
2.426
1.292
1.24
1.016
1.153
0.8913
1.305
3.421
2.04
1.175
1.563
1.385
1.483
1.408
1.989
1.383
1.385
1.086
1.121
1.055
0.9517
1.414
1.31
1.173
0.9445
0.8422
0.9537
1.134
1.046
0.9893
1.153
0.9136
107.7
79.65
134.4
22.74
20.5
9.678
6.947
5.059
10.13
4.842
6.526
56.58
20.23
18.38
23.09
15.97
12.22
10.77
14.84
8.159
11.11
3.165
5.649
35.13
28.66
71.24
39.41
44.42
43.83
59.1
66.17
12.93
4.785
2.049
8.772
1.397
10.47
7.87
12.91
2.653
2.457
1.546
1.43
1.138
1.615
1.135
1.276
5.717
2.45
2.25
2.72
2.098
1.795
1.666
1.989
1.488
1.637
0.9653
1.317
3.751
3.149
7.057
4.112
4.591
4.559
5.913
6.61
1.818
1.128
1.02
1.46
1.011
139.7
78.26
40.83
38.83
64.84
57.54
15.3
2.654
13.37
30.28
15.11
36.88
132.8
74.53
95.45
57.99
66.71
61.91
73.36
54.66
66.13
23.26
28.79
10.96
9.833
9.403
10.43
13.29
20.53
2.818
22.27
1.738
3.678
23.42
95.32
9.657
13.39
7.693
4.211
4.027
6.423
5.748
1.927
0.8102
1.739
3.23
1.876
3.842
12.74
7.31
9.278
5.798
6.601
6.152
7.211
5.48
6.53
2.564
3.125
1.524
1.41
1.393
1.455
1.734
2.373
0.8537
2.562
0.8128
0.885
2.618
9.236
1.426
                                                 284
-------
PSAPCA
FINE FILTER

SDATE

891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108

STIME

725
1800
630
1851
643
1847
641
1842
636
1855
650
1840
652
1845
710
1840
641
1845
646
1838
645
1840
705
1919
714
1915
711
1912
700
1845
0
1845
645
1830
640
1845

BR
NG/H3
10.31
5.41
2.709
6.922
12.96
3.27
1.133
1.024
1.975
17.69
5.046
6.423
17.93
21.73
14.46
12.13
11.98
19.66
14.35
23.21
12.09
3.946
5.379
2.217
2.481
0.5203
3.118
3.876
2.482
0.7023
3.289
-0.4565
2.126
1.644
2.808
2.331
ERROR
BR
NG/M3
1.327
1.031
0.7535
1.066
1.539
0.7743
0.7668
0.6238
0.8291
1.938
0.91
1.05
2.019
2.312
1.697
1.524
1.514
2.141
1.697
2.461
1.441
0.8195
0.9934
0.7521
0.7668
0.6611
0.7261
0.7921
0.7748
0.6179
0.8352
0.6449
0.6914
0.7632
0.786
0.8418

SR
NG/M3
0.9866
1.578
0.9374
2.572
0.4876
0.991
1.263
1.565
0.3144
0.3576
0.2424
-0.867
1.24
1.344
4.434
2.633
7.652
7.045
1.996
1.494
2.074
1.147
-0.6129
1.279
0.0232
0.4404
0.6978
2.282
0.9337
0.9636
0.31
0.9045
0.0845
1.042
1.931
1.401
ERROR
SR
NG/M3
0.8025
0.9351
0.7289
0.8678
0.7851
0.7823
0.9012
0.7418
0.8368
0.7417
0.7278
0.7299
0.8202
0.8327
0.9935
0.9154
1.198
1.182
0.8633
0.8777
0.797
0.7159
0.8412
0.796
0.7178
0.7344
0.6966
0.8017
0.7691
0.7019
0.7952
0.7855
0.7016
0.8009
0.8089
0.8187

BA
NG/M3
51.12
34.95
22.61
18.5
20.33
13.62
27.3
1.504
24.57
0.9743
15.09
14.97
32.75
23.45
20.89
20.7
43.78
7.66
18.32
12.98
34.41
7.944
23.14
19.03
9.736
21.17
-2.272
25.65
11.3
14.19
25.43
16.17
5.514
10.13
2.369
26.02
ERROR
BA
NG/M3
11
10.89
9.414
9.792
9.812
9.681
10.6
8.969
10.14
8.857
9.219
9.11
10.04
9.624
10.22
10.02
11.02
9.627
9.868
9.812
9.913
8.729
10.33
9.403
9.123
9.474
8.52
9.582
9.076
8.628
10.11
9.4
8.846
9.54
8.987
10.06

PB
NG/M3
40.03
17.78
15.11
30.52
48.25
16.21
24.24
7.19
15.17
47.47
26.93
24.37
92.19
65.74
55.77
31.3
69.19
51.16
45.25
48.19
32.11
19.1
20.11
10.01
5.94
4.527
28.47
10.21
11.29
7.095
11.21
1.817
5.538
3.837
25.21
14.38
ERROR
PB
NG/M3
4.5
2.806
2.359
3.672
5.197
2.534
3.276
1.804
2.531
5.098
3.325
3.13
9.193
6.756
5.902
3.793
7.115
5.495
4.967
5.246
3.79
2.617
2.933
2.093
1.794
1.733
3.377
2.075
2.162
1.785
2.2
1.717
1.715
1.799
3.172
2.432
                                                 285
-------
Site

MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
MORSE
Date

05-Dec-89
05-Dec-89
06-Dec-89
06-Dec-89
07-Dec-89
07-Dec-89
08-Dec-89
08-Dec-89
09-Dec-89
09-Dec-89
10-Dec-89
IO-Dec-89
11-Dec-89
11-Dec-89
12-Dec-89
12-Dec-89
13-Dec-89
13-Dec-89
H-Dec-89
U-Dec-89
15-Dec-89
15-Dec-89
02-Jan-90
02-Jan-90
03-Jan-90
03-Jan-90
04-Jan-90
04-Jan-90
05-Jan-90
05-Jan-90
06-Jan-90
06-Jan-90
07-Jan-90
07-Jan-90
08-Jan-90
08-Jan-90
Teflon
Start- Duration
Time
822
1912
700
1922
724
1915
718
1924
702
1917
718
1910
716
1915
728
1900
707
1915
706
1858
708
1902
737
1944
738
1958
737
1945
725
1945
745

720
1915
705
1900
(min)
665.1
706.5
726.2
719.4
708.2
721.0
722.7
694.2
732.8
720.8
702.7
726.7
715.2
739.7
694.1
708.4
730.7
706.3
709.6
727.7
711.7
712.9
713.6
710.9
731.3
695.2
730.7
698.1
715.0
736.0
693.2
717.1
710.5
705.2
721.9
718.0
Fine Organic Elemental
Mass Carbon Carbon
1C
N03-
1C
S04--
ug/m**3 ug/m**3 ug/m**3 ug/m**3 ug/m**3
23.71
17.89
14.43
28.76
37.77
7.61
4.60
4.31
9.94
43.48
26.32
43.40
56.84
65.39
69.64
22.73
34.05
40.98
45.57
42.79
29.78
16.24
21.95
11.98
6.82
5.55
7.00
18.23
12.26
17.04

3.15
6.09
7.93
13.82
16.36
10.40
7.98
4.54
11.76
11.94
3.54
3.09
1.88
5.47
22.08
12.88
19.63
25.33
36.51
29.54
8.97
15.70
19.90
20.34
19.75
13.08
3.88
10.70
5.54
3.29
2.92
3.07
6.53
4.13
2.66
5.14
1.36
1.63
2.07
5.83
5.94
3.30
1.97
2.25
1.60
2.68
0.76
1.12
0.58
1.24
2.13
1.26
1.55
3.38
3.58
4.42
1.54
3.79
3.96
4.49
2.91
2.50
0.74
3.39
0.78
0.89
0.54
1.03
0.87
1.81
0.61
1.32
0.10
0.44
0.38
3.36
1.75
1.14
0.88
1.17
1.62
1.35
0.39
0.26
0.21
0.51
1.19
1.76
2.61
3.20
2.53
4.08
2.38
3.01
1.80
2.60
2.08
2.26
1.63
0.83
0.58
0.32
0.40
0.26
1.01
0.44
0.25
0.64
0.22
0.24
0.31
0.46
0.81
1.11
1.33
2.05
3.25
3.04
0.74
0.50
0.32
0.68
1.51
2.48
2.65
5.68
5.22
6.36
1.92
3.59
3.14
4.53
3.79
4.01
2.25
1.45
1.13
0.81
0.63
0.60
0.93
0.94
0.34
0.90
0.10
0.28
1.51
0.94
0.81
286
-------
MORSE
FINE FILTER
ERROR ERROR ERROR
SDATE STIME GMAS GMAS AL AL SI SI S
ERROR ERROR
S CL CL
NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/H3 NG/M3 NG/H3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
822
1912
700
1922
724
1915
718
1924
702
1917
718
1910
716
1915
728
1900
707
1920
710
1901
711
1905
737
1944
738
1958
737
1945
725
1945
745
0
720
1915
705
1900
23710
17880
14480
28780
37780
7613
4601
4314
9985
43460
26310
43380
56860
65360
69700
22740
34040
40990
45540
42770
29810
16240
21940
11980
6826
5552
6917
18020
12260
17090
5953
3155
6083
7927
13820
16400
1901
1788
1741
1758
1786
1753
1748
1822
1725
1753
1798
1739
1768
1708
1822
1786
1729
1791
1780
1736
1775
1773
1781
1778
1729
1819
1729
1811
1779
1718
1824
1763
1778
1793
1751
1761
176
6.682
77.14
-8.246
142.1
21.44
-8.614
-5.65
-31.76
220.5
50.08
34.59
73.38
94.36
215.7
35.45
211.2
132.1
88.11
67.77
118.2
19.36
34.12
45.67
-29.66
•19.15
46.17
841.7
465.8
894.1
587.8
206.1
181.9
25.37
59.48
50.79
49.31
39.85
37.28
38.59
46.22
35.65
35.6
32.88
33.52
55.8
38.34
39.57
45.16
46.51
62.21
38.28
57.29
45.58
44.48
41.56
41.53
35.39
36.59
35.12
31.63
33.08
31.96
132.2
80.77
138.5
96.59
48.31
46.01
38.12
38.02
38.49
70.92
13.55
57.26
39.33
111
26.84
43.09
19.52
6.297
58.16
48.79
74.62
120.1
101.7
399.1
106.6
135
119.8
204.7
75.66
104.4
65.66
116.2
28.08
55.5
32.45
76.75
52.83
51.19
60.07
14.39
2.404
18.34
5.809
58.9
22.01
17.91
14.2
15.31
15.86
22.4
13.27
14.9
12.14
12.16
17.45
15.74
18.28
24.75
22.68
61.01
21.11
26.27
23.71
33.95
18.96
21.07
16.77
21.88
12.98
14.6
13.3
16.19
15.32
15.35
15.21
13.35
11.99
12.61
13.28
16.01
13.77
603.7
605.6
659.5
1227
1520
273.2
173.4
148.8
222.9
575.9
1065
1055
2106
1671
2542
928
1152
1298
1712
1635
1621
1105
635.4
413.7
329.6
204.3
257.8
451.9
375.9
172.9
314
91.23
168
534.7
359.4
350
46.89
46.75
50.42
92.32
114.9
21.97
22.46
13.41
18.8
46.17
80.64
80.01
159.6
126.8
191.4
70.3
88.3
98.74
130.3
123.8
121.9
83.09
49.28
32.12
26
16.88
21.28
34.9
29.67
14.64
25.28
9.192
14.32
41.62
28.9
27.66
251.9
556.5
140
317.9
284.3
133.6
249.4
287.4
183.7
336.2
148.2
330
386
479.9
550.9
154.9
226.4
174.7
208.8
205.6
94.54
24.3
74.66
112.4
122.3
13.56
97.48
97.47
88.85
295.6
129.4
511.5
659.4
331.6
168.4
159.8
19.67
41.88
11.46
24.41
22.12
10.96
23.26
22.05
14.54
25.97
12.16
25.35
29.77
36.58
41.92
12.63
18.06
14.23
16.79
16.42
8.77
4.29
7.653
9.521
10.09
3.507
8.418
8.484
7.959
22.58
10.8
38.38
49.27
25.48
13.58
12.89
287
-------
MORSE
FINE FILTER
SDATE STIME K
ERROR ERROR ERROR ERROR
K CA CA TI TI V V
NG/M3 NG/M3 NG/M3 NG/H3 NG/M3 NG/M3 NG/M3 NG/H3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
822
1912
700
1922
724
1915
718
1924
702
1917
718
1910
716
1915
728
1900
707
1920
710
1901
711
1905
737
1944
738
1958
737
1945
725
1945
745
0
720
1915
705
1900
163.2
347.8
137.1
173
225.6
164.8
136.2
71.23
95.51
277.1
171.6
231.3
233.9
376.6
310.4
180.8
175.9
212.6
185.4
210.9
129.6
96.15
98.33
83.84
45.55
90
119.1
168.6
69.26
31.03
82.96
29.08
38.82
283.7
214
127.7
12.55
26.02
10.62
13.24
17.07
12.63
10.59
6.029
7.668
20.86
13.14
17.48
17.7
28.17
23.35
13.8
13.53
16.11
14.17
15.99
10.09
7.774
7.884
6.872
4.257
7.282
9.278
12.91
5.905
3.38
6.856
3.389
3.916
21.3
16.21
9.982
62
20.25
40.11
30.43
69.96
13.55
31.13
17.87
23.6
30.08
72.39
44.46
110.3
43.34
94.6
43.96
108.3
48.84
91.77
33.64
84.1
22.08
41
21.85
27.66
13.96
22.07
23.88
23.79
17.69
23.03
15.79
25.71
22.9
38.96
34.34
5.667
3.531
4.266
3.903
6.067
3.245
3.937
3.206
3.444
3.891
6.223
4.484
8.848
4.515
7.908
4.565
8.817
4.714
7.588
3.887
7.044
3.508
it. 297
3.424
3.533
3.141
3.182
3.538
3.718
3.258
3.557
3.229
3.537
3.558
4.299
4.035
2.534
4.272
6.694
6.253
8.093
-13.62
4.017
3.392
0.982
3.361
6.239
10.08
7.252
8.361
10.56
13.62
-5.223
12.53
12.42
6.955
6.584
3.426
5.199
1.789
11.76
3.638
7.091
2.734
-7.619
2.273
2.184
0.117
1.12
1.346
8.86
1.863
4.531
4.779
3.929
5.096
3.857
5.119
4.877
4.133
4.972
4.312
4.216
4.22
6.86
4.149
6.06
4.337
4.9
5.161
4.356
5.144
3.892
4.42
4.406
4.915
3.994
5.134
3.711
4.493
6.152
5.16
4.094
4.002
4.129
4.08
5.014
4.117
0.974
1.549
6.832
14.84
11.62
-3.123
0.949
2.26
0.649
3.257
8.644
8.787
12.35
8.446
18.66
7.784
2.356
5.96
12.54
9.996
15.08
5.094
2.248
0.414
2.65
1.546
3.818
0.959
-10.65
0.674
3.362
1.52
1.578
16.25
3.703
4.804
1.656
3.987
2.039
4.758
1.994
3.96
1.707
2.467
4.413
2.749
2.963
2.976
2.748
2.266
6.494
1.8
2.553
4.745
2.455
5.06
2.406
1.678
3.008
4.474
1.659
1.763
1.436
2.924
6.81
1.749
1.781
1.59
2.246
2.273
4.572
1.592
ERROR
CR CR
NG/H3 NG/M3
9.03
6.921
6.482
4.239
21.73
3.597
12.94
1.27
0.5638
0.8743
5.072
0.4251
8.463
3.833
16.13
3.162
6.78
1.085
67.48
11.91
8.727
-0.3261
24.77
-0.8951
0.8157
0.8782
6.468
3.435
1.72
1.362
2.106
0.4439
0.4827
1.618
4.292
2.064
1.175
1.276
1.006
1.229
2.266
1.083
1.487
0.7461
1.078
0.8244
0.9958
0.8176
1.147
0.8541
2.207
0.7622
1.118
1.155
6.47
1.716
1.169
0.6139
2.582
1.062
0.6188
0.624
0.9226
0.9172
1.625
0.5927
0.7142
0.6187
0.6921
0.6969
1.216
0.7026
                                                 288
-------
HORSE
FINE FILTER
ERROR ERROR ERROR ERROR ERROR
SDATE STIME MN MN FE FE NI NI CU CU ZN ZN
NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
822
1912
700
1922
724
1915
718
1924
702
1917
718
1910
716
1915
728
1900
707
1920
710
1901
711
1905
737
1944
738
1958
737
1945
725
1945
745
0
720
1915
705
1900
52.42
21.61
64.25
31.75
55.11
14.34
38.63
5.935
16.13
30.04
26.8
13.31
64.02
42.48
66.02
21.17
51.71
42.8
84.4
41.2
29.15
8.593
39.99
6.902
28.92
4.325
42.02
9.175
22.34
6.106
11.63
1.06
4.774
3.293
45.66
14.16
4.115
1.959
4.954
2.735
4.272
1.471
3.13
0.8963
1.603
2.572
2.305
1.392
4.904
3.401
5.128
1.902
4.095
3.438
6.348
3.331
2.464
1.082
3.236
1.002
2.432
0.8357
3.328
1.135
2.165
0.882
1.267
0.6901
0.847
0.8136
3.636
1.492
399
139.7
474
178.4
467.7
98.69
210.2
24.39
52.11
105.4
181.9
69.14
366.9
212.3
423.7
96.87
349.8
175.7
867.6
235
183.6
45.81
383.9
29.89
129.6
28.09
257.9
63.04
165.4
14.28
37.73
5.314
7.403
20.59
237.9
67.82
37.95
13.83
44.87
17.4
44.29
10.02
20.35
3.351
5.796
10.68
17.72
7.308
34.9
20.52
40.23
9.854
33.32
17.13
81.55
22.62
17.86
5.255
36.51
3.873
12.83
3.715
24.73
6.78
16.21
2.563
4.547
2.04
2.153
3.085
22.91
7.228
11.22
7.362
7.81
9.386
30.61
1.003
4.349
1.832
0.1333
2.756
6.959
1.968
17.83
5.848
26.41
2.686
8.976
3.507
95.2
27.73
19.47
0.7242
30.45
-0.7984
0.4403
0.7559
5.523
4.356
7.789
1.086
1.589
-1.605
-0.6665
8.841
5.703
0.6013
1.759
1.422
1.467
1.608
3.391
0.9802
1.23
0.9368
0.9207
1.145
1.363
1.017
2.275
1.309
3.099
1.074
1.656
1.085
9.369
3.145
2.398
0.9301
3.407
0.8467
0.8888
0.9295
1.185
1.154
1.485
0.9165
1.003
0.8196
0.884
1.532
1.26
1.02
13.03
10.11
13.2
6.146
14.3
4.447
5.577
2.11
4.082
8.546
7.789
5.961
17.12
10.83
17.23
5.735
15.31
7.109
26.31
7.713
8.618
3.861
13.56
2.171
4.598
1.494
7.683
7.291
6.376
1.535
3.486
2.088
0.1469
2.829
7
1.231
1.86
.593
.824
.317
.894
.182
1.278
0.9487
1.119
1.51
1.403
1.24
2.155
1.643
2.261
1.241
2.086
1.31
3.012
1.395
1.434
1.12
1.876
1.022
1.092
0.9711
1.317
1.357
1.349
0.9345
1.095
1.012
0.9086
1.076
1.326
1.013
79.82
32.98
67.55
56.92
73.96
47.73
34.55
4.341
17.56
31.14
34.38
33
97.99
80.07
106.7
30.44
81
80.37
82.53
69.6
54.25
25.94
33.62
8.905
27.02
5.888
52.11
10.36
14.33
5.34
14.45
0.808
5.432
10.65
43.1
12.31
7.841
3.497
6.661
-5.693
7.265
4.837
3.636
0.9352
2.079
3.329
3.621
3.476
9.496
7.825
10.32
3.248
7.925
7.852
8.073
6.854
5.435
2.837
3.54
1.345
2.918
1.092
5.217
1.469
1.839
1.034
1.816
0.7496
1.048
1.501
4.402
1.652
                                                 289
-------
MORSE
FINE FILTER
ERROR ERROR ERROR ERROR
SDATE STIME BR BR SR SR BA BA PB PB
NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/H3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
8912H
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
822
1912
700
1922
724
1915
718
1924
702
1917
718
1910
716
1915
728
1900
707
1920
710
1901
711
1905
737
1944
738
1958
737
1945
725
1945
745
0
720
1915
705
1900
8.531
5.782
3.528
8.292
14.59
3.051
3.07
0.9398
4.746
15.02
9.821
9.748
18.83
22.21
20.35
8.958
12.18
17.34
18.73
20.88
9.386
3.435
8.687
5.402
4.837
1.598
2.667
4.216
4.982
2.625
3.857
1.237
1.973
0.7313
6.129
4.304
1.213
1.036
0.8165
1.187
1.68
0.7929
0.8066
0.6511
0.9217
1.743
1.247
1.258
2.066
2.358
2.229
1.198
1.569
1.918
2.051
2.227
1.247
0.8844
1.199
0.9684
0.8748
0.7153
0.7299
0.866
0.9488
0.7594
0.9094
0.7405
0.777
0.7364
1.004
0.9291
-2.815
-1.131
1.413
6.941
2.907
1.28
0.9265
0.4293
0.067
2.138
-0.0314
-0.363
1.901
8.128
1.59
1.418
3.516
6.552
1.205
1.634
1.563
1.056
0.9044
1.647
0.8221
4.554
1.826
2.414
1.649
1.553
0.4669
1.087
1.051
3.305
4.185
1.975
0.7646
0.7721
0.7907
1.133
0.7923
0.8169
0.8448
0.7135
0.7658
0.887
0.7518
0.7463
0.8255
1.167
0.9275
0.7828
1.028
1.032
0.8066
0.8121
0.7727
0.8027
0.7944
0.8096
0.7285
0.9349
0.7211
0.8193
0.8678
0.7781
0.7777
0.8066
0.7921
0.8911
0.9013
0.8696
31.53
18.97
7.506
18.89
12.55
41.96
15.88
17.12
26.09
1.191
8.844
3.627
29.32
13.49
18.2
27.97
37.91
26.21
21.67
23.19
19.13
11.66
24.65
22.38
15.77
17.98
17.34
29.17
19.72
20.22
10.49
15
14.94
23.69
18.44
18.27
10.3
9.745
9.135
9.917
9.01
10.51
9.83
9.385
9.77
9.577
9.276
9.024
9.791
9.496
10.42
9.771
11.11
9.466
9.696
9.402
8.985
9.613
9.574
9.565
8.933
9.682
8.686
9.904
10.07
9.333
9.73
9.654
9.475
9.824
9.513
9.972
34.24
24.29
18.6
22.75
53.25
9.593
159.9
19.33
22.24
70.24
31.35
32.05
91.53
72.19
75.39
24.35
65.45
59.14
68.95
51.28
39.39
17.82
38.48
12.18
13.33
6.551
28.06
8.284
15.28
6.645
20.73
1.594
5.147
30.79
32.13
13.53
4.028
3.175
2.718
3.109
5.595
2.117
15.4
2.714
3.001
7.184
3.741
3.756
9.101
7.346
7.699
3.142
6.811
6.149
7.051
5.457
4.386
2.639
4.332
2.272
2.223
1.888
3.337
2.007
2.56
1.873
2.866
1.657
1.824
3.69
3.774
2.416
                                                 290
-------
Appendix E-3.  Coarse-Particle Results
NOTE:  Due to  a computer programming error  discovered in early  1991,  the attentuation
corrections for dichot coarse  Mn,  Fe,  Co, Ni,  Cu,  and Zn were not calculated into the
coarse-particle  data as reported  from  the laboratory.   The reported  values are  low by
approximately 5% for Fe, 7% for Co, Ni, Cu, and Zn, and less than 6% for Mn.  Because the
corrections would be approximate and less that one standard deviation, the data have not been
corrected for this error.
                                          291
-------
MORSE
COARSE FILTER
ERROR ERROR ERROR
SDATE STIME GMAS GMAS AL AL SI SI S
S
ERROR ERROR
CL CL
NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/H3 NG/M3 NG/M3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
822
1912
700
1922
724
1915
718
1924
702
1917
718
1910
716
1915
728
1900
707
1920
710
1901
711
1905
737
1944
738
1958
737
1945
725
1945
745
0
720
1915
705
1900
11320
5496
8285
6616
17790
2312
5172
1294
4597
4457
1883
5052
15920
13130
24180
5845
19700
10740
30450
9459
14930
4927
14430
4866
2512
134
3609
24960
20430
5776
20140
12880
10420
3624
8238
2029
1711
1609
1567
1582
1607
1578
1574
1639
1552
1578
1618
1565
1591
1537
1639
1607
1556
1612
1602
1563
1598
1596
1603
1600
1556
1637
1556
1630
1601
1546
1642
1587
1600
1614
1576
1585
281.7
13.6
843.9
739.2
723.6
272.9
188.9
57
222.5
82.3
572.9
690.1
1294
451.4
1926
343.8
1191
771.2
1925
579.8
824.2
395
446.8
140.1
50.9
-43.2
142.6
10440
5337
4661
7811
4389
2944
92.8
416.7
145.9
114.3
58.36
252.8
219.3
225.8
99.09
83.96
61.51
88.49
68.17
179.4
208.5
381
150.8
567
120
360.3
238.4
560.4
181.9
252.9
130.1
151.4
77.5
60.25
55.7
71.42
3008
1542
1371
2249
1260
850.3
70.55
139.6
70.55
710.5
137.1
392.9
272.7
1470
92.95
264.8
31.67
425.3
584.8
346.8
457.1
2475
1282
3939
736
3398
2249
4943
1614
2440
830
2016
404
341.4
132
493.7
457.7
295.9
84.5
219
47.07
47.95
-23.08
498.1
119.5
181.1
41.22
102.5
72.77
370
31.64
71.68
22.3
108.3
149.3
91.36
119
618
323.3
990.9
188.8
846.6
562.3
1231
403.5
608.5
209.6
505.1
104.6
89.98
39.92
127.5
119
79.1
31.42
60.4
24.23
24.84
21.82
128.8
36.5
138.4
125.8
131.1
241
174.6
57.19
91.25
74.9
87.55
96.38
130.8
169.7
233.3
351.7
257.2
90.74
222.2
168.8
296.6
237.6
179.1
124.9
143.2
88.87
65.5
27.76
40.49
265.9
166.9
95.09
167.8
138.4
138.3
115.4
100.1
57.98
27.91
25.81
27.35
48.38
45.98
12.94
15.95
13.62
16.53
22.4
33.13
37.43
61.94
69.5
71.3
26.47
46.31
42.49
64.28
55.19
47.77
32.45
29.51
19.01
14.91
9.097
11.02
40.78
27.3
17.16
26.9
19.81
21.13
23.99
19.84
14.31
405.1
227.8
135.9
22.83
51.17
318.4
831.2
1146
1107
150.3
49.6
25.15
63.27
41.32
89.69
33.57
122.8
28.93
130
11.08
65.27
16.92
790
1054
441.1
103.7
174.4
742
297.7
492.1
595.1
1229
1436
966.4
306.3
49.91
47.71
32.62
17.36
8.173
10.75
36.64
93.33
127.7
122.1
21.56
8.771
8.374
13.35
12.18
18.39
7.237
17.41
7.743
18.15
6.364
9.866
4.501
86.76
115.5
49.68
12.33
20.8
81.8
33.98
57.6
66.39
139.6
163.8
109
36
8.671
293
-------
MORSE
COARSE  FILTER
SDATE STIME K
ERROR ERROR ERROR ERROR ERROR
K CA CA TI TI V V CR CR
NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/H3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
822
1912
700
1922
724
1915
718
1924
702
1917
718
1910
716
1915
728
1900
707
1920
710
1901
711
1905
737
1944
738
1958
737
1945
725
1945
745
0
720
1915
705
1900
68.01
144.6
35
48.4
89.25
74.82
48.16
44.19
56.62
52.73
29.14
43.93
118.5
92.03
200.4
39.08
148.2
101.4
230.6
84.95
109.9
48.8
126.1
47.79
25.74
38.22
39.65
51.04
36.92
23.12
36.3
36.26
33.7
52.73
48.34
27.54
9.539
19.31
6.459
7.609
12.3
10.1
7.231
6.066
7.504
9.24
5.804
7.838
15.34
14.35
24.55
6.828
17.63
13.37
26.09
11.68
13.24
6.787
14.51
6.549
4.072
5.718
6.144
7.851
5.37
3.641
5.527
4.799
4.678
9.385
8.168
5.073
224.4
49.69
168.6
129.9
370.9
29.5
163.2
46.86
118
99.67
250.6
121.7
576.7
236
774.3
235.7
910.6
343
867.4
210
538.5
149.6
324.1
145.4
170.9
74.01
136
73.55
112.7
39.96
73.95
37.7
52.13
162.4
209.8
54.88
19.02
5.145
14.68
11.24
30.72
3.801
13.85
4.943
10.2
8.848
21.15
10.66
47.56
19.69
63.24
19.69
74.27
28.32
70.67
17.57
44.26
12.69
26.74
12.36
14.37
6.831
11.6
6.937
9.837
4.335
6.981
4.261
5.295
13.69
17.59
5.575
13.38
11.64
8.105
11.31
34.44
6.085
1.395
3.45
8.718
4.435
-7.285
6.143
51.33
23.99
82.19
21.19
99.96
34.75
112.8
39.06
49.42
7.329
67.4
28.21
26.86
-7.089
14.62
9.627
15.46
3.293
2.698
1.228
3.094
0.46
30.02
6.712
6.246
4.054
5.472
3.949
10.19
3.599
5.135
3.807
it. 292
4.802
5.884
4.621
9.778
6.208
15.96
5.808
14.22
8.062
17.93
6.745
9.257
5.436
10.65
6.646
5.551
4.999
4.256
3.953
4.407
3.445
5.027
3.486
3.51
3.739
5.778
3.93
-1.587
1.125
-1.226
5.26
-1.942
0.192
-1.907
2.224
-0.614
-0.269
-13.72
-0.189
2.065
-0.082
2.245
1.981
10.22
0.052
4.722
4.846
4.563
-1.961
2.511
1.518
0.509
-3.037
0.113
1.63
3.974
-0.513
-2.563
-0.222
-0.282
4.327
1.689
1.897
4.34
1.41
4.671
1.732
2.646
1.4
3.043
1.458
2.277
3.271
5.781
2.558
2.439
1.614
3.144
4.69
3.316
1.84
2.276
2.107
2.313
1.659
1.903
1.874
2.961
4.455
2.4
1.515
2.55
1.363
3.061
1.282
1.393
2.044
1.514
1.439
5.566
15.75
4.07
2.703
16.44
6.278
16.54
2.307
0.498
1.313
-1.2
2.077
7.86
3.625
6.702
2.498
6.61
2.264
41.34
5.31
4.765
2.001
14.12
1.846
3.118
-0.2758
11.33
8.593
8.219
2.869
4.41
2.6
2.123
0.2604
4.542
0.7522
1.476
2.358
1.34
0.8072
2.675
1.149
2.6
0.758
0.7381
0.9111
1.386
0.8171
1.492
0.9108
1.463
1.227
1.383
0.8266
6.576
1.213
1.149
0.7315
2.433
0.7061
0.9632
1.074
1.836
1.453
1.426
0.7658
1.128
0.7404
0.7166
0.7123
1.005
0.6194
                                                 294
-------
MORSE
COARSE FILTER
ERROR ERROR ERROR ERROR ERROR
SDATE STIME MN MN FE FE NI NI CU CU ZN ZN
NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
8912U
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
822
1912
700
1922
724
1915
718
1924
702
1917
718*
1910
716
1915
728
1900
707
1920
710
1901
711
1905
737
1944
738
1958
737
1945
725
1945
745
0
720
1915
705
1900
14.48
8.273
11.59
5.574
20.02
2.636
13.11
1.408
5.478
8.496
6.089
6.488
26.19
21.82
27.44
8.414
25.59
20.8
41.43
17.18
14.32
5.348
20.7
5.645
8.467
3.117
7.459
5.105
6.272
1.936
6.17
1.857
2.639
1.616
11.12
4.13
2.299
1.415
2.116
1.323
2.697
0.8963
1.953
0.8118
1.126
1.588
1.393
1.153
3.282
2.665
3.438
1.449
3.099
2.645
4.674
2.299
2.062
1.137
2.627
1.044
1.487
0.8873
1.524
1.038
1.283
0.7581
1.207
0.7345
0.7926
0.7786
1.905
0.953
748.9
249.6
602.3
235.4
1033
88.18
325.3
63.57
154.5
264.8
262.1
221
999.6
572.2
1219
262
1024
702.7
1644
533.1
632.5
197.6
840.7
169.1
270.5
96.35
334.5
148.9
186.7
51.68
112
21.55
39.84
32.51
438
83.43
74.36
25.28
61.39
24.32
101.5
9.903
33
6.972
15.56
26.34
26.86
21.91
97.37
56.01
118.4
26
99.45
67.83
162.4
52.59
61.36
19.52
82.81
16.72
27.1
9.984
34.31
15.19
19.69
5.724
11.55
3.047
4.614
4.149
43.78
9.16
3.03
8.571
2.136
3.362
10.83
1.576
6.945
-0.0221
0.7281
0.4435
2.013
2.001
6.22
4.145
6.896
1.442
5.124
2.486
24.27
2.481
4.335
-0.6198
8.056
-0.5066
0.8915
0.7756
7.002
10.19
4.287
0.632
1.031
1.26
2.428
0.5338
0.4212
-0.4305
1.161
1.483
1.015
1.087
1.904
0.9161
1.342
0.8438
0.807
0.8348
1.01
0.8844
1.444
1.113
1.623
0.8984
1.222
1.042
3.744
1.179
1.301
0.78
1.707
0.8128
0.8395
0.8606
1.314
1.611
1.14
0.7804
0.9926
0.8304
0.9001
0.8942
0.8998
0.7667
10.3
3.249
6.173
2.198
10.69
1.878
3.805
-0.877
4.032
3.507
2.731
2.119
10.68
4.1
19.29
0.4344
15.49
8.114
45.4
4.618
13.69
1.676
7.642
2.35
4.578
2.158
4.181
27.5
14.6
9.814
18.43
11.18
6.372
0.9841
11.38
1.263
1.672
1.078
1.284
0.953
1.666
0.936
1.086
0.8165
1.033
1.043
1.01
0.9027
1.714
1.113
2.487
0.8895
2.069
1.427
4.913
1.128
1.904
0.9172
1.463
0.9342
1.102
0.9201
1.085
3.092
1.916
1.444
2.269
1.582
1.166
0.8746
1.674
0.8594
19.23
12.88
35.68
21.57
27.24
8.262
12.39
2.547
7.706
10.44
15.42
10.27
55.38
47.11
51.27
11.38
44.58
35.76
60.75
58.05
29.24
10.96
23.53
3.348
11.37
17.01
26.26
10.52
12.12
2.975
6.679
2.941
3.21
2.559
35.57
3.892
3.001
1.925
4.344
2.945
3.636
1.667
1.911
0.8307
1.328
1.682
2.166
1.679
6.48
5.518
6.202
1.775
5.291
4.495
6.836
6.433
3.64
1.709
2.913
0.9319
1.732
2.046
3.315
1.54
1.678
0.8241
1.265
0.8238
0.8158
0.8735
4.104
0.9556
                                                 295
-------
MORSE
COARSE  FILTER
ERROR ERROR ERROR ERROR
SDATE STIME BR BR SR SR BA BA PB PB
NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
8912H
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
822
1912
700
1922
724
1915
718
1924
702
1917
718
1910
716
1915
728
1900
707
1920
710
1901
711
1905
737
1944
738
1958
737
1945
725
1945
745
0
720
1915
705
1900
0.8922
1.163
1.155
0.4274
1.219
0.4472
1.405
3.83
2.744
1.181
1.235
1.118
0.0784
3.018
0.8155
0.9932
1.465
0.3967
2.119
1.88
-0.1664
0.266
0.5331
0.583
1.259
-0.1355
0.4542
0.826
-0.2417
1.306
1.598
2.369
3.95
1.547
1.777
0.4628
0.7254
0.6229
0.6134
0.6354
0.6857
0.6138
0.6735
0.7734
0.7172
0.697
0.7024
0.6443
0.732
0.8762
0.8208
0.6793
0.7001
0.7294
0.8291
0.785
0.6658
0.6312
0.7367
0.6612
0.5988
0.6205
0.579
0.6893
0.6026
0.6137
0.7233
0.7146
0.7424
0.6882
0.7229
0.6034
2.611
2.682
0.4194
1.113
5.725
-0.2127
0.5921
0.0965
1.83
1.671
1.384
2.298
7.415
4.107
8.61
2.273
12.5
6.924
18.3
4.526
7.708
1.835
8.724
2.768
1.638
1.106
0.3547
1.725
1.181

0.4463
1.689
0.9297
1.475
1.935
1.097
0.8156
0.7724
0.6796
0.7232
0.9734
0.7039
0.7381
0.7125
0.715
0.7264
0.7208
0.7065
1.109
0.8758
1.198
0.7723
1.404
1.066
1.877
0.8736
1.122
0.756
1.2
0.792
0.7095
0.7326
0.6722
0.7684
0.6973
0.6458
0.7538
0.7118
0.6592
0.75
0.782
0.711
33.16
10.09
27.2
15.35
37.72
7.293
40.57
19.74
8.591
30.57
33.88
28.62
31.88
28.55
45.88
22.97
16.22
36.35
36.49
22.96
27.94
36.41
16.54
20.15
7.668
35.16
-2.812
8.298
19.26
11.12
32.86
2.706
9.093
11.88
18.12
6.908
9.877
8.638
8.541
8.387
9.514
8.422
9.679
8.879
8.15
8.789
9.326
8.513
9.41
8.875
10.32
8.799
8.513
9.723
9.509
8.728
9.198
9.385
9.189
8.762
8.173
9.291
8.007
8.704
8.548
8.026
9.836
8.25
8.198
8.632
8.825
8.342
11.26
4.775
6.593
6.811
20.54
1.601
-8.563
0.8499
9.378
9.787
5.857
6.58
18.4
23.88
23.85
6.154
19.15
22.2
30.55
21.47
13.52
3.139
17.89
4.456
4.163
3.844
0.936
14.39
4.964
24.95
5.704
2.477
4.291
5.73
11.57
4.335
2.381
1.81
1.804
1.854
3.142
1.574
1.801
1.598
2.013
2.403
1.89
1.85
3.343
3.559
3.708
1.851
3.119
3.387
4.184
3.183
2.544
1.695
2.889
1.707
1.634
1.58
1.553
2.371
1.704
3.089
1.928
1.499
1.556
1.886
2.323
1.652
                                                 296
-------
PSAPCA
COARSE FILTER
ERROR ERROR ERROR
SDATE STIME GMAS GMAS AL AL SI SI S
S
ERROR ERROR
CL CL
NG/M3 NG/H3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
725
1800
630
1851
643
1847
641
1842
636
1855
650
1840
652
1845
710
1840
641
1845
646
1838
645
1840
705
1919
714
1915
711
1912
700
1845
0
1845
645
1830
640
1845
8848
5313
6965
5421
13660
1216
2710
1516
1470
6020
3662
694.6
19290
9360
18820
7037
17240
9596
20010
16270
12790
3322
9739
2296
2929
-93.3
3419
4388
2299
1963
5226
3605
1948
2047
2248
2697
1661
1614
1569
1609
1571
1612
1587
1600
1552
1593
1614
1563
1614
1537
1668
1600
1571
1602
1602
1580
1598
1574
1606
1602
1580
1596
1571
1621
1652
1519
1649
1614
1571
1621
1556
1618
123.2
219.9
241.2
874.9
998.5
335.4
36.6
19.4
-73
79.4
302.9
-1275
1284
170.5
1153
386.2
949.4
362.9
1572
608.7
883.5
151.5
403.5
-558
16.4
-1.8
14.8
-13.8
196
183.8
22.4
85.9
-45.5
103.2
71.1
74.5
79.68
87.19
94.36
258.7
300.5
119.8
62.19
61.39
62
64.01
114.9
66.02
387.2
81.46
359.3
158.9
296.6
177.6
463.2
190.5
282.8
73.82
135.8
66.41
57.14
52.54
57.68
62.8
83.54
90.87
61.57
66.94
55.21
64.1
58.21
61.32
687.2
259.3
462.1
334.1
1315
100.9
111.9
-15.37
229.9
501.2
192.2
205.7
2547
694.2
2821
1036
3201
1785
3234
1787
2302
487.5
1401
179.7
207.1
29.92
416.7
230.8
236.7
13.7
104.3
22.36
25.55
13.29
163.9
39.84
177.3
68.94
118.3
88.57
331.3
33.69
35.28
19.98
63.74
127.5
52.73
58.88
634.6
175.9
704
261
796.2
446.1
804.9
445.8
576.7
124.9
350.9
53.06
56.08
19.8
108.4
63.15
63.57
19.53
36.48
21.23
20.4
19.41
46.75
22.34
178.2
106.3
151.7
163.5
318.2
120.1
69.3
77.15
83.14
71.06
181.9
101.2
420.4
372.3
365.9
117.2
272.5
191.9
413.9
400.6
287.5
119.8
160.5
88.52
101.2
61.08
86.66
179.8
125.3
50.75
96.9
81.49
112.6
97.38
59.79
62.18
33.57
25.94
30.05
34.15
65.55
28.59
20.79
15.87
14.78
18.96
37.65
26.31
90.66
71.77
73.84
29.05
51.27
41.77
77.74
73.39
58.26
31.1
29.09
18.39
21.53
14.34
20.91
30.96
23.37
11.97
17.1
17.26
22.1
16.59
14.19
13.53
476.9
107.5
124.9
46.23
71.08
215.5
732.7
1142
1108
145.5
51.63
4.89
65.92
44.65
75.5
54.46
80.56
22.01
65.72
57.55
70.43
9.25
734.6
751.2
459.3
60.29
111.1
445.3
182.1
473.1
402
1231
1347
543.8
278.7
74.99
55.21
15.88
15.73
8.92
13.17
24.55
80.44
126.1
122.5
20.93
8.008
5.802
15.52
13.14
14.59
9.65
12.03
8.232
10.54
10.21
10.74
4.29
80.68
83.03
50.48
7.945
13.2
49.28
20.78
52.98
44.94
136.4
150.7
60.39
32.64
10.51
297
-------
PSAPCA
COARSE  FILTER
SDATE STIME K
ERROR ERROR ERROR ERROR
K CA CA TI TI V V
NG/M3 NG/H3 NG/M3 NG/M3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
725
1800
630
1851
643
1847
641
1842
636
1855
650
1840
652
1845
710
1840
641
1845
646
1838
645
1840
705
1919
714
1915
711
1912
700
1845
0
1845
645
1830
640
1845
53.15
42.38
43.22
37.35
81.58
24.05
29.03
33.32
43.42
44.09
21.82
26.92
119.1
62.71
131.1
57.07
139
83.72
146.9
99.64
103
30.34
83.36
32.99
25.99
8.788
25.82
38.15
29.1
19.44
25.48
34.59
40.6
27.09
20.6
31.92
7.509
6.62
6.175
6.072
11.54
4.192
4.236
4.546
5.859
8.555
4.492
5.687
15.45
11.43
16.52
8.194
16.27
11.55
17.14
12.68
12.44
5.712
9.792
4.925
3.936
2.827
4.005
6.137
4.546
3.329
4.975
4.616
5.215
4.438
3.952
5.15
241.5
100.7
297.1
168.5
457.2
154.3
120.5
52.78
105
85.94
145
31.91
658.1
103.4
752.8
296.9
772.7
330.3
641
303.6
579.4
92.83
273.6
66.93
105.8
29.35
177.8
217.7
88.64
25.66
83.05
48.56
47.38
85.74
82.91
50.11
20.55
8.883
24.54
14.25
37.57
13.31
10.45
5.304
9.209
7.715
12.34
4.131
53.78
9.159
61.49
24.59
63.18
27.18
52.26
24.97
47.43
8.231
22.74
6.44
9.249
3.749
14.94
18.57
8.093
3.543
7.739
4.988
4.866
7.664
7.574
5.198
46.65
22.66
10.63
16.88
41.25
8.84
9.245
2.785
7.19
10.83
8.208
5.405
55.89
20.27
63.58
28.42
74.73
44.88
81.91
34.87
58.9
1.181
30.97
6.095
8.784
0.892
14.47
7.579
9.901
4.243
3.56
0.3575
1.282
3.731
23.78
2.397
10.45
4.784
5.292
4.426
8.427
4.455
3.982
4.18
3.932
3.945
4.638
4.787
11.5
5.354
11.33
6.007
16.17
8.053
13.44
7.766
10.16
4.702
6.972
3.721
3.741
3.587
4.968
4.02
4.519
3.835
4.154
4.86
3.497
3.486
4.824
3.737
NG/H3 NG/H3
-1.522
-0.0146
-0.963
4.363
4.42
2.958
1.977
-0.3981
1.427
2.945
1.958
1.979
3.198
1.848
4.516
3.235
1.014
4.309
8.049
3.677
5.841
-2.091
-0.5412
0.7852
2.787
5.094
4.97
4.744
3.576
0.8934
0.5524
3.369
2.26
0.6286
2.219
1.545
2.318
1.703
2.835
1.613
2.546
3.328
1.62
3.428
1.901
1.69
4.116
4.469
2.631
1.661
2.803
3.992
3.504
1.946
3.108
2.833
2.175
2.378
1.606
1.367
2.121
1.894
3.972
1.864
3.175
2.434
2.762
1.813
2.371
1.725
1.507
1.45
ERROR
CR CR
NG/H3 NG/M3
3.547
3.284
3.615
2.065
8.704
1.011
2.2
-0.5218
0.0879
0.9415
1.06
0.4953
10.38
0.4465
5.547
1.2
3.443
3.116
4.778
2.944
3.65
0.502
2.154
0.2294
1.329
0.4959
2.475
2.651
2.059
-0.0416
1.074
-0.1901
0.04
-0.1371
1.248
0.3538
0.9284
0.877
1.035
0.7568
1.544
0.9351
0.7801
0.9068
0.6784
0.6988
1.067
1.12
1.721
0.6477
1.228
l'.063
0.9299
0.8574
1.143
0.9519
0.9414
0.7594
0.7606
0.6424
0.7363
0.6849
1.102
0.8137
0.9509
0.7479
0.8473
0.605
0.7146
0.6194
0.6546
0.6699
                                                 298
-------
PSAPCA
COARSE FILTER
ERROR ERROR ERROR ERROR ERROR
SDATE STIME MN MN FE FE NI NI CU CU ZN ZN
NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/H3 HG/M3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
891214
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
725
1800
630
1851
643
1847
641
1842
636
1855
650
1840
652
1845
710
1840
641
1845
646
1838
645
1840
705
1919
714
1915
711
1912
700
1845
0
1845
645
1830
640
1845
8.268
3.773
7.454
6.002
15.44
2.655
5.129
0.5308
3.09
7.381
2.989
2.642
26.63
10.89
22.3
12.35
21.17
13.74
21.98
24.74
21.76
5.45
11.28
2.188
2.859
0.7644
4.117
3.869
4.873
-0.0297
2.451
1.572
-0.0639
2.922
5.151
0.8206
1.595
1.03
1.29
1.256
2.142
0.8844
1.065
0.753
0.9266
1.378
0.9328
0.954
3.227
1.797
2.866
1.854
2.679
2.066
2.939
2.891
2.614
1.095
1.665
0.7937
0.8227
0.7186
0.9912
0.9304
1.149
0.6955
0.9295
0.7174
0.6522
0.8091
1.173
0.7911
397.8
155.2
389.2
199.8
693.7
52.43
160.9
28.74
89.18
171.6
67.7
58.35
913.4
206.9
915.6
306.4
850.3
497.2
982.6
483.7
737.9
122.7
548.1
124
149.7
36.75
177.9
107.3
210.1
28.49
86.44
13.74
21.44
18.06
314.5
57.03
39.64
15.82
38.44
20.31
68.63
6.032
16.28
3.74
9.414
17.15
7.308
7.056
89.86
21.19
88.6
30.6
82.29
48.31
95.9
46.93
71.66
12.59
53.93
12.83
14.98
4.436
17.88
11.29
21.39
3.678
10.01
2.434
2.965
2.805
33.22
6.606
0.5743
2.08
0.6006
1.987
7.909
1.299
0.4298
0.7391
0.8887
-0.1938
2.531
-1.23
5.769
1.875
5.773
-0.1285
3.646
2.54
6.748
3.201
4.491
0.412
0.4603
2.431
0.7523
2.955
2.776
1.8
0.8266
1.611
1.799
-0.4379
1.451
0.6466
-0.5718
1.295
0.9358
0.9704
0.9131
0.9903
1.573
0.993
0.9237
0.8827
0.8821
0.7885
1.013
0.943
1.351
0.9397
1.391
0.8967
1.151
1.05
1.443
1.114
1.195
0.8765
0.8441
0.9583
0.8419
1.08
1.057
0.9686
0.9206
0.912
0.9507
0.7912
0.8385
0.7965
0.7442
0.9628
39.57
32.27
68.22
9.991
16.39
6.567
7.595
1.221
3.221
1.454
2.155
-4.42
12.49
4.008
13.48
6.177
10.15
4.655
16.7
8.585
11.46
-0.3964
9.294
24.6
16.35
43.12
25.81
23.39
20.67
21.13
33.91
7.023
4.474
2.133
1.769
2.757
5.185
4.223
8.069
1.706
2.245
1.329
1.386
0.9007
1.039
0.9052
0.9654
0.9097
1.887
1.154
2.066
1.347
1.629
1.184
2.207
1.471
1.726
0.8177
1.456
3.081
2.263
5.126
3.234
3.071
2.836
2.995
4.25
1.357
1.041
0.8868
0.8944
1.038
34.47
20.03
16.63
21.02
37.1
5.958
2.607
2.36
3.147
6.408
6.444
3.722
54.76
41.56
74.6
13.9
56.96
37.41
56.81
107.9
40.22
9.711
20.39
1.308
6.589
2.118
8.625
4.358
9.43
1.013
3.579
0.75
0.466
5.064
15.69
2.915
4.981
3.03
2.361
2.736
4.461
1.583
0.9461
0.7916
0.9396
1.329
1.221
1.187
6.772
4.946
8.258
2.264
6.311
4.455
6.371
10.92
4.759
1.569
2.578
0.8304
1.173
0.8687
1.37
1.063
1.549
0.7355
1.102
0.6702
0.6183
1.158
2.77
0.9268
                                                 299
-------
PSAPCA
COARSE FILTER
ERROR ERROR ERROR ERROR
SDATE STIME BR BR SR SR BA BA PB PB
NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3 NG/M3
891205
891205
891206
891206
891207
891207
891208
891208
891209
891209
891210
891210
891211
891211
891212
891212
891213
891213
8912U
891214
891215
891215
900102
900102
900103
900103
900104
900104
900105
900105
900106
900106
900107
900107
900108
900108
725
1800
630
1851
643
1847
641
1842
636
1855
650
1840
652
1845
710
1840
641
1845
646
1838
645
1840
705
1919
714
1915
711
1912
700
1845
0
1845
645
1830
640
1845
2.801
0.7364
0.9914
0.4372
0.7095
-0.2318
2.681
4.219
1.246
1.1
0.0592
1.178
0.657
3.084
1.882
-0.0394
1.562
-0.0865
1.156
2.794
1.422
0.6723
2.8
-0.1176
-0.9835
0.4031
-0.6771
1.386
1.276
1.408
1.861
2.772
1.552
1.333
0.8378
0.7166
0.7975
0.6316
0.6225
0.6263
0.7465
0.6466
0.7484
0.7755
0.6584
0.7187
0.6578
0.6529
0.7514
0.8603
0.8045
0.6568
0.7279
0.7003
0.7431
0.8889
0.6851
0.6174
0.738
0.6654
0.561
0.6096
0.6176
0.6559
0.6654
0.6489
0.7244
0.7411
0.6582
0.612
0.5855
0.6549
3.359
0.8928
4.357
3.875
5.872
1.816
1.223
1.972
2.269
1.856
1.01
1.396
6.542
0.618
9.968
2.673
11.27
6.013
6.109
5.471
5.094
1.39
3.491
1.905
0.8626
0.336
0.5129
2.545
1.792
1.161
2.508
1.146
1.318
1.385
0.0975
-0.467
0.8786
0.7031
0.8703
0.8563
1.014
0.7892
0.7697
0.7476
0.7691
0.7353
0.733
0.7252
1.008
0.6746
1.37
0.8058
1.426
1
1.004
0.9571
0.922
0.7547
0.7876
0.7791
0.6871
0.6967
0.7182
0.8241
0.7714
0.7286
0.7906
0.7093
0.6684
0.6895
0.6432
0.7269
29.5
11.95
30.8
12.09
29.53
7.794
10.32
8.424
14.5
16.22
13.86
20.54
33.62
13.71
30.06
5.677
47.34
21.77
27.53
32.17
23.47
36.24
29.68
-3.385
0.4556
3.378
24.84
20.54
17.69
11.03
15.3
17.68
1.226
1.531
13
1.579
9.69
8.624
9.181
8.641
9.401
8.943
8.821
8.495
8.673
8.375
8.679
8.683
9.352
8.167
9.969
8.448
10.01
8.764
9.161
9.221
8.954
9.362
8.778
8.583
7.927
8.362
8.91
8.972
9.022
8.35
8.947
8.767
7.758
8.051
7.853
8.796
8.612
6.77
3.881
4.894
11.63
3.371
0.9798
1.311
1.642
10. 84
1.655
2.967
20.8
18.03
19.19
9.603
8.837
14.96
17.56
28.96
12.66
5.191
12.6
1^881
4.609
1.588
1.821
3.803
4.729
1.248
3.592
0.5236
-1.208
2.546
4.158
4.3
2.19
1.857
1.673
1.837
2.481
1.727
1.66
1.517
1.587
2.32
1.66
1.677
3.516
3.01
3.187
2.201
2.394
2.702
2.866
3.854
2.394
1.799
2.227
1.572
1.641
1.546
1.686
1.666
1.784
1.535
1.698
1.428
1.301
1.503
1.651
1.808
                                                300
-------
Appendix E-4. VOC Results
                                    301
-------
   ORGflNICS LIST
S
                      COMPOUND
 BHI-037  Bni-030  BHI-039  BHI-22   BMI-035   BHI-4   BMI-13   BHI-16   BUI-038   02194   BHI-23    02155
  HORSE    MORSE   PSflPCfl   PSflPCfl    HORSE    MORSE   PPSPCfl   PSflPCfl    MORSE    MORSE   PSflPCfl   PSflPCfl
  flM MR   1920 MR  0705 MR  1842 HR  0715 HR  1917 HR  0630 HR  1842 HR  0721 HR  1919 HR  0634 HR  1830 HR
12/05/89 12/05/89 12/05/89 12/05/89 12/06/89 12/06/89 12/06/89 12/06/89 12/07/89 12/07/89 12/07/89 12/07/89
1) dichlorodifluoromethane
2) methyl chloride *
3) l,2-dichloro-l,l,2,2-tetrafluoroethane
4) vinyl chloride
5) methyl bromide
6) ethyl chloride
7) trichlorofluoromt thane
8) 1,1-dichloroethene
9) dichloromethane
10) 3-ch 1 or opropene
11) l,l,2-trichloro-l,2,2-trifluoroethane
12) 1,1-dichloroethane
13) cis-l,2-dichloroethene
14) trichloromethane
15) 1,2-dichloroethane
16) 1,1,1-trichloroethane
17) benzene
18) carbon tetrachloride
19) 1,2-dichloropropane
20) trichloroethene
21) 2,2,4-trimethylpentane

it.) cis— 1,0— oicnior opropene

£.3> trans— 1,0,— aicnior opropene
24) 1,1,2-trichloroethane
25) toluene
26) 1,2-dibromoethane
27) tetrachloroethene
J)A\ i 1 t
£ot cn lorooenzene
29) ethylbenzene
30) m+p-xylene
31) styrene
32) 1,1,2,2-Uirachloromthane
33) o-xylene
34) 4-ethyltolu*nt
35) l,3,5-trimethylb*nrene
36) 1,2,4-trimethylbenzene
37) benzyl chloride
*^«*V 1 • 1 1 1_
38) m— a icn lorooenzene
__K j • _i_ i ^
jy^ p— a i cn i orooenzene
40) o-dichlorobenzene
41) 1,2,4-trichlorobenzene
42) hexachlorobutadiene
0.59
<0.10
<0.10
<0.10
<0.10
<0.10
1.08
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.61
3.71
0.11
<0.10
<0.10
0.58
<0.10
<0.10
<0.10
7.22
<0.10
0.20
<0.10
1.17
4.30
0.22
<0.10
1.55
0.43
0.45
1.31
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.61
0.38
<0.10
<0.10
<0.10
<0.10
0.96
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.45
3.02
0.12
<0.10
<0.10
0.24
<0.10
<0.10
<0.10
5.34
<0.10
0.16
<0.10
0.71
2.68
0.26
<0.10
0.97
0.28
0.28
0.85
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.16
<0.10
<0.10
<0.10
<0.10
<0.10
0.90
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.61
2.61
0.17
<0.10
<0.10
0.40
<0.10
<0.10
<0.10
5.76
<0.10
0.36
<0.10
1.62
6.35
0.25
<0.10
2.14
0.50
0.42
1.26
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.73
2.00
<0.10
<0.10
<0.10
<0.10
1.06
<0.10
0.56
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.45
2.03
0.10
<0.10
<0.10
0.17
<0.10
<0.10
<0.10
4.07
<0.10
0.17
<0.10
0.63
2.35
0.59
<0.10
0.90
0.28
0.23
0.73
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.56
<0.10
<0.10
<0.10
<0.10
<0.10
0.82
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.45
2.00
0.12
<0.10
<0.10
0.30
<0.10
<0.10
<0.10
3.96
<0.10
0.16
<0.10
0.70
2.68
<0.10
<0.10
0.96
0.23
0.26
0.75
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.75
<0.10
<0.10
<0.10
<0.10
<0.10
0.89
<0.10
<0.10
<0.10
0.21
<0.10
<0.10
<0.10
<0.10
0.75
2.75
0.12
<0.10
<0.10
0.50
<0.10
0.26
<0.10
6.01
<0.10
0.16
<0.10
1.41
4.17
0.52
<0.10
1.51
0.49
0.45
1.41
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.87
<0.10
<0.10
<0.10
<0.10
<0.10
0.87
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.50
1.16
0.14
<0.10
<0.10
0.17
<0.10
<0.10
<0.10
2.87
<0.10
<0.10
<0.10
0.52
2.03
4.61
<0.10
0.75
0.17
0.16
0.45
<0.10
<0.10
<0.10
<0.10
<0.10
<0. 10
0.85
<0.10
<0.10
<0.10
<0.10
<0.10
0.94
<0.10
0.18
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.79
1.82
0.13
<0.10
<0.10
0.18
<0.10
<0.10
<0.10
4.27
<0.10
0.22
<0.10
0.86
2.74
2.61
<0.10
0.99
0.16
0.27
0.86
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
25.17
<0.10
<0.10
<0.10
<0.10
<0.10
1.15
<0.10
0.57
<0.10
0.19
<0.10
<0.10
<0.10
<0.10
1.10
4.73
<0.10
<0.10
<0.10
0.68
<0.10
0.26
<0.10
12.10
<0.10
0.31
<0.10
1.58
5.75
0.47
<0.10
2.12
0.52
0.47
1.72
<0.10 ,
<0.10
<0.10
<0.10
<0.10
<0.10
0.47
<0.10
<0.10
<0.10
<0.10
<0.10
0.70
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.40
1.08
0.12
<0.10
<0.10
0.12
<0.10
<0.10
<0.10
1.95
<0.10
<0.10
<0.10
0.24
0.94
<0.10
<0.10
0.28
<0.10
0.26
0.16
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.95
<0.10
<0.10
<0.10
<0.10
<0.10
1.01
<0.10
0.43
<0.10
0.36
<0.10
<0.10
<0.10
<0.10
0.95
3.76
0.14
<0.10
<0.10
0.52
<0.10
0.34
<0.10
8.14
<0.10
0.27
<0.10
1.82
6.88
0.38
<0.10
2.38
0.52
0.47
1.42
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.59
<0.10
<0.10
<0.10
<0.10
<0.10
0.81
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.27
0.92
0.11
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.57
<0.10
<0.10
<0.10
0.22
0.79
<0.10
<0.10
0.34
<0.10
<0.10
0.23
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
    *  Instrument Difficulties in Resolving this Compound.
-------
    ORGflNICS LIST
                      COMPOUND
  02136   BHI-036   02138   BHI-15    BM1-6   BHI-027  BHI-24   BMI-14   BMI-B48  BMI-033  BMI-19   BMI-B12
  HORSE    MORSE   PSRPCfl   PSflPCfl    MORSE    MORSE   PSflPCfl   PSflPCfl     MORSE    MORSE   PSflPCH   PSflPCfi
 0715 HR  1919 HR  0635 HR  1836 HR  0658 HR  1913  HR  0642  HR  1850 HR  0722 HR  1925 HR  0650 HR  1835 HR
12/08/89 12/08/89 12/08/89 12/08/89 12/09/89 12/09/89  12/09/89  12/09/89  12/10/89  12/10/89  12/10/89  12/10/89
    1)  dichlorodifluoroAethane
    2)  methyl  chloride *
    3)  l,2-dichloro-l,l,2,2-tetr*fluoroeth*ne
    4)  vinyl chloride
    5)  methyl  bromide
    6)  ethyl chloride
    7)  trichlorofluoromethane
    8)  1,1-dichloroethene
    9)  dichloromethane
    10) 3-chloropropene
    11) l,l,2-trichloro-l,2,2-trifluoroethane
    12) 1,1-dichloroethane
    13) cis-l,2-dichloroethene
    14) trichloromethane
    15) 1,2-dichloroethane
    16) 1,1,1-trichloroethane
    17) benzene
    18) carbon tetrachloride
(jj  19) 1,2-dichloropropaoe
g  20) trichloroethene
    21) 2,2,4-trimethylpentane
    22) cis-l,3-dichloropropene
    23) trans-l,3,-dichloropropene
    24) 1,1,2-trichloroethane
    25) toluene
    26) l,2-dibro*oeth«ne
    27) tetrachloroethene
    28) chlorobenzene
    29) ethylbenzene
    30) m+p-xylene
    31) styrene
    32) 1,1,2,2-tetrachloroethane
    33) o-xylen*
    34) 4-ethyltoluww
    35) 1,3,5-triMthyllMnzOTW
    36) l,2,4-tri«ethylb*nzene
    37) benzyl  chloride
    38) iti-di chlorobenzene
    39) p-dichlorobenzene
    40) o-dichlorobenzene
    41)  1,2,4-trichlorobenzene
    42)  hexachlorobutadiene
0.47
<0.10
<0.10
<0.10
<0.10
<0.10
0.94
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.20
1.50
0.12
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
3.42
<0.10
<0.10
<0.10
0.45
1.77
<0.10
<0.10
0.68
0.28
0.24
0.70
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.33
<0.10
<0.10
<0.10
<0.10
<0.10
0.64
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.26
0.66
0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.29
<0.10
<0.10
<0.10
0.28
0.89
<0.10
<0.10
0.37
<0.10
0.19
0.21
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.43
<0.10
<0.10
<0.10
<0.10
<0.10
0.71
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.42
1.36
0.14
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
2.35
<0.10
<0.10
<0.10
0.28
1.04
<0.10
<0.10
0.28
0.16
<0.10
0.30
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
9.90
0.36
<0.10
<0.10
<0.10
<0.10
0.99
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.18
0.32
0.11
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.59
<0.10
<0.10
<0.10
<0.10
0.31
<0.10
<0.10
0.11
<0.10
0.11
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.66
<0.10
<0.10
<0.10
<0.10
<0.10
0.85
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.78
2.28
0.10
<0.10
<0.10
0.38
<0.10
<0.10
<0.10
3.86
<0.10
<0.10
<0.10
0.54
1.91
<0.10
<0.10
0.75
0.21
0.23
0.70
<0.10
<0.10
<0.10
<0.10
<0. 10
<0.10
0.63
<0.10
<0.10
<0.10
<0.10
<0.10
0.92
<0.10
0.42
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
0.50
4.29
0.12
<0.10
<0.10
0.66
<0.10
0.33
<0.10
7.40
<0.10
<0.10
<0.10
1.03
3.69
0.35
<0.10
1.48
0.45
0.40
1.29
<0. 10
<0.10
<0.10
<0.10
<0.10
<0.10
0.31
<0.10
<0.10
<0.10
<0.10
<0.10
0.71
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.28
0.82
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.32
<0.10
<0.10
<0.10
0.23
0.66
0.23
<0.10
0.30
0.10
0.16
0.28
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.63
<0.10
<0.10
<0.10
<0.10
<0.10
1.25
<0.10
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
<0.10
0.57
4.10
0.12
<0.10
<0.10
0.54
<0.10
0.28
<0.10
6.99
<0.10
<0.10
<0.10
1.01
3.69
0.31
<0.10
1.34
0.42
0.38
1.15
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.67
<0.10
<0.10
<0.10
<0.10
<0.10
0.83
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.83
2.34
0.11
<0.10
<0.10
0.31
<0.10
<0.10
<0.10
3.44
<0.10
<0.10
<0.10
0.54
1.82
<0.10
<0.10
0.72
0.11
0.18
0.58
<0.10
<0.10
<0.10
<0.10
<0. 10
<0. 10
1.51
<0.10
<0.10
<0.10
<0.10
<0.10
0.79
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.38
2.43
0.11
<0.10
<0.10
0.29
<0.10
<0.10
<0.10
3.57
<0.10
<0.10
<0.10
0.52
1.75
<0.10
<0.10
0.65
0.16
0.16
0.54
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.50
<0.10
<0.10
<0.10
<0.10
<0.10
0.76
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.31
1.60
<0.10
<0.10
<0.10
0.20
<0.10
<0.10
<0.10
2.38
<0.10
<0.10
<0.10
0.29
1.26
2.56
<0.10
0.49
0.13
0.11
0.34
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
2.47
0.49
<0.10
<0.10
<0.10
<0.10
0.95
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.36
2.12
0.11
<0.10
<0.10
0.23
<0.10
<0.10
<0.10
2.90
<0.10
<0.10
-------
   ORGRNICS LIST
8
                      COMPOUND
BMI-26   BMI-029  BMI-ll   BMI-18    8HI-7   LC0016   BMI-045  LC0055   LC0023   LCOOSO   LC0035   LC0008
 MORSE    MORSE   PSflPCfl   PSRPCfl    MORSE    MORSE   PSRPCfl   PSRPCfl    MORSE    MORSE   PRSPCfl   PSRPCfl
0716 HR  1916 HR  0730 HR  1930 HR  0725 HR  1915 HR  0720 HR  1835 HR  0708 HR  1915 HR  0634 HR  1841 HR
        12X11X89 12/11/89 12X11X89 12/12/09 12/12/89 12/12/89 12X12X89 12X13X89 12X13X89 12x13x89 12X13x89
1) dichlorodifluoroMethane
2) Methyl chloride *
3) l,2-dichloro-l,l,2,2-tetr*fluoroeth«ne
4) vinyl chloride
5) Methyl broMide
6) ethyl chloride
7) trichlorof luoroMethane
8) 1,1-dichloroethene
9) dichloroMethane
i n\ ^ L i
i iw o~cn i Or opr opcnc
11) l,l,2-trichloro-l,2,2-trifluoroethane
12) 1,1-dichloroethane
13) cis-l,2-dichloroethene
14) trichloroMethane
15) 1,2-dichloroethane
16) 1,1,1-trichloroethane
17) benzene
18) carbon tetrachloride
19) 1,2-dichloropropane \
20) trichloroethene
21) 2,2,4-triMethylpentane
*^*>\ * t "i j * 1 1
£.£.) cis-i jo— oicnioropropene
23) tr«ns-l,3,-dichloropropene
24) 1,1,2-trichloroethane
25) toluene
26) 1,2-dibroMoethane
27) tetrachloroethene
OO\ l_ 1 L.
£ot cnioroDenzene
29) ethylbenzene
30) M+p-xylene
31) styrene
32) l,l,2,2-tetr*chloroethane
33) o-xylene
34) 4-ethyltoluent
35) 1,3,5-triMethylbenzene
36) 1,2,4-triMethylbenzene
37) benzyl chloride
38) ffl-dichlorobenzene
39) p-dichlorobenzene
40) o-dichlorobenzene
41) 1,2,4-trichlorobenzene
42) hexachlorobutadiene
0.87
<0.10
<0.10
<0.10
<0.10
<0.10
0.85
<0.10
<0.10
<0.10
0.23
<0.10
<0.10
<0.10
<0.10
0.90
5.79
0.10
<0.10
<0.10
0.40
<0.10
0.42
<0.10
11.30
<0.10
0.23
<0.10
1.70
6.41
0.54
<0.10
2.23
0.56
0.50
1.69
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.83
<0.10
<0.10
<0.10
<0.10
<0.10
0.99
<0.10
0.82
<0.10
0.31
<0.10
<0.10
<0.10
<0.10
1.11
7.98
0.12
<0.10
<0.10
1.13
<0.10
0.38
<0.10
14.67
<0.10
0.37
<0.10
1.86
7.11
0.90
<0.10
2.62
0.66
0.66
2.12
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.16
<0.10
<0.10
<0.10
<0.10
<0.10
0.99
<0.10
0.57
<0.10
0.26
<0.10
<0.10
<0.10
<0.10
1.20
6.40
0.12
<0.10
<0.10
0.96
<0.10
0.50
<0.10
13.00
<0.10
0.52
<0.10
1.72
6.55
1.74
<0.10
2.38
0.63
0.56
1.86
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.46
<0.10
<0.10
<0.10
<0.10
<0.10
1.10
<0.10
1.04
<0.10
0.35
<0.10
<0.10
<0.10
<0.10
1.22
6.59
0.10
<0.10
<0.10
0.87
<0.10
0.47
<0.10
11.96
<0.10
0.33
<0.10
1.56
5.89
1.36
<0.10
2.19
0.57
0.52
1.70
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.03
<0.10
<0.10
<0.10
<0.10
<0.10
0.95
<0.10
0.54
<0.10
0.27
<0.10
<0.10
<0.10
<0.10
1.08
7.04
0.11
<0.10
<0.10
0.99
<0.10
<0.10
<0.10
13.32
<0.10
0.34
<0.10
1.96
7.35
0.79
<0.10
2.65
0.68
0.59
2.03
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.71
0.69
<0.10
<0.10
<0.10
<0.10
0.79
<0.10
0.15
<0.10
0.32
<0.10
<0.10
<0.10
<0.10
0.59
2.72
0.13
<0.10
<0.10
0.40
<0.10
<0.10
<0.10
5.63
<0.10
0.24
<0.10
0.86
3.09
0.35
<0.10
1.09
0.30
0.29
0.84
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.01
<0.10
<0.10
<0.10
<0.10
<0.10
0.90
<0.10
0.73
<0.10
0.24
<0.10
<0.10
<0.10
<0.10
1.55
4.46
0.11
<0.10
<0.10
0.63
<0.10
<0.10
<0.10
9.49
-------
ORGflNICS LIST
                  COMPOUND
 1) dichlorodifluoromethane
 2) methyl chloride *
 3) l,2-dichloro-l,l,2,2-tetrafluoroethane
 4) vinyl chloride
 5) «eihyl bromide
 6) ethyl chloride
 7) trichlorofluoromethane
 8) 1,1-dichloroethene
 9) dichloromethane
 10) 3-chloropropene
 11) l,l,2-trichloro-l,2,2-trifluoroethane
 12) 1,1-dichloroethane
 13) cis-l,2-dichloroethene
 14) trichloromethane
 15) l,2-dichloroeth*n«
 16) 1,1,1-trichloroethane
 17) benzene
 18) carbon tetrachloride
 19) 1,2-dichloropropane
 20) trichloroethene
 21) 2,2,4-trimethylpentan*
 22) cis-l,3-dichloropropen*
 23) trans-l,3,-dichloropropene
 24) 1,1,2-trichloroethane
 25) toluene
 26) l,2-dibro*oethane
 27) tetrachloroethene
 28) chlorobenzene
 29) ethylbenzene
 30) m+p-xylene
 31) styrene
 32) l,l,2,2-t*tr*chloro*than*
 33) o-xylen«
 34) 4-ethyltolucrw
 35) l,3,5-tri«*thu,lb«nz«n»
 36) 1,2,4-trimethylbenzene
 37) benzyl chloride
 38) m-dichlorob*nz«n*
39) p-dichlorobenzen«
40) o-dichlorobenzene
41) 1,2,4-trichlorobenzene
42) hexachlorobutadiene
LC0053 LC0067 LC0002
MORSE MORSE PSflPCfl
0706 HR 1858 HR 0640
LC0004 LC0061 LC0058 LC0015 LC0011 LC0062 LC0051 LC0014 LC0060
PSflPCfl HORSE MORSE PSflPCfl PSflPCfl MORSE MORSE PSflPCfl PSflPCfl
1833 HR 0708 HR 1900 HR 0638 HR 1837 HR 0735 HR 1940 HR 0717 HR 1918 HR
12X14X89 12X14X89 21x14X89 12X14x89 12X15X89 12X15x89 12X15x89 12X15x89
1.01
<0.10
<0.10
<0.10
<0.10
<0.10
0.83
<0.10
0.73
<0.10
0.23
<0.10
<0.10
<0.10
<0.10
0.83
6.43
0.14
<0.10
<0.10
0.89
<0.10
<0.10
<0.10
15.26
<0.10
0.28
<0.10
2.54
9.70
0.82
<0.10
3.34
0.80
0.80
2.42
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.71
<0.10
<0.10
<0.10
<0.10
<0.10
0.82
<0.10
1.62
<0.10
0.10
<0.10
<0.10
<0.10
<0.10
1.36
5.72
0.10
<0.10
<0.10
0.80
<0.10
<0.10
<0.10
11.46
<0.10
0.21
<0.10
1.70
6.59
0.82
<0. 10
2.26
0.70
0.63
1.95
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.22
<0.10
<0.10
<0.10
<0.10
<0.10
0.87
<0.10
0.64
<0.10
0.24
<0.10
<0.10
<0.10
<0.10
1.22
4.05
0.12
<0.10
<0.10
0.64
<0.10
<0.10
<0.10
8.41
<0.10
0.14
<0.10
1.39
5.27
2.29
<0.10
1.98
0.56
0.57
1.86
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.92
<0.10
<0.10
<0.10
<0.10
<0.10
0.92
<0.10
2.24
<0.10
0.43
<0.10
<0.10
<0.10
<0.10
1.81
5.79
0.14
<0.10
<0.10
0.83
<0.10
<0.10
<0.10
12.60
<0.10
0.35
<0.10
1.79
7.02
2.68
<0.10
2.45
0.66
0.68
1.96
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.70
<0.10
<0.10
<0.10
<0.10
<0.10
0.71
<0.10
0.57
<0.10
0.23
<0.10
<0.10
<0.10
<0.10
0.76
2.69
0.10
<0.10
<0.10
0.37
<0.10
<0.10
<0.10
5.72
<0.10
0.17
<0.10
0.92
3.51
0.38
<0.10
1.23
0.33
0.30
1.01
<0. 10
<0.10
<0.10
<0.10
<0.10
<0.10
0.49
0.28
<0.10
<0.10
<0.10
<0.10
0.61
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.42
1.15
0.12
<0.10
<0.10
0.10
<0.10
<0.10
<0.10
2.05
<0.10
<0.10
<0.10
0.31
1.27
<0.10
<0.10
0.42
0.12
0.16
0.35
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.85
<0.10
<0.10
<0.10
<0.10
<0.10
0.78
<0.10
0.52
<0.10
0.28
<0.10
<0.10
<0.10
<0.10
0.87
2.46
0.10
<0.10
<0.10
0.35
<0.10
<0.10
<0.10
5.62
<0.10
0.23
<0.10
0.90
3.57
0.78
<0.10
1.25
0.31
0.33
1.08
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.42
<0.10
<0.10
<0.10
<0.10
<0.10
0.63
<0.10
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
<0.10
0.28
0.75
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.25
<0.10
<0.10
<0.10
0.21
0.76
<0.10
<0.10
0.26
<0.10
<0.10
0.26
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1X02X90
0.34
0.34
<0.10
<0.10
<0.10
<0.10
0.58
<0.10
0.28
<0.10
0.16
<0.10
<0.10
<0.10
<0.10
0.89
3.16
0.12
<0.10
<0.10
0.43
<0.10
<0.10
<0.10
6.35
<0.10
0.12
<0.10
1.02
3.65
0.27
<0.10
1.30
0.35
0.32
0.99
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1X02X90
0.52
0.31
<0.10
<0.10
<0.10
<0.10
0.47
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.15
1.02
0.12
<0.10
<0.10
0.10
<0.10
<0.10
<0.10
1.73
<0.10
<0.10
<0.10
0.25
0.%
<0.10
<0.10
0.37
0.12
0.12
0.32
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1X02X90
0.52
0.23
<0.10
<0.10
<0.10
<0.10
0.53
<0.10
<0.10
<0.10
0.18
<0.10
<0.10
<0.10
<0.10
0.27
2.05
<0.10
<0.10
<0.10
0.26
<0.10
<0.10
<0.10
3.79
<0.10
0.11
<0.10
0.63
2.26
0.52
<0.10
0.78
0.21
0.21
0.72
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1X02X90
0.55
0.40
<0.10
<0.10
<0.10
<0.10
0.50
<0.10
0.16
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
0.21
0.80
0.13
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.97
<0.10
<0.10
<0.10
0.15
0.28.
0.10
<0.10
0.19
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
* Instrument Difficulties in Resolving this Compound.
-------
ORGflNICS LIST
                  COMPOUND
LC0029   LC0032   LC0038   LCOCH6   LC0068   LC0045   LC0022   LC0071   LCOCK8   LC0019   LC0065   LC0075
 MORSE    MORSE   PflSPCfl   PSRPCfl    MORSE    MORSE   PSflPCfl   PSRPC9    MORSE    MORSE   PSflPCfl   PSflPCfl
0739 HR  1953 HR  0710 HR  1927 HR  0733 HR  1947 HR  0710 HR  1915 HR  0732 HR  1920 HR  0650 HR  1855 HR
1/03/90  1/03/90  1/03/90  1/03X90  1/04/90  1/04/90  1/04x90  1/04/90  1/05/90  1/05/90  1/05/90  1/05/90
1) dichlorodifluoroaethane
2) methyl chloride *
3) l,2-dichloro-l,l,2,2-tetrafluoroeth»ne
4) vinyl chloride
5) methyl bronide
6) ethyl chloride
7) trichlorofluoroaethane
8) 1,1-dichloroethene
9) dichlorooiethane
10) 3-chloropropene
11) l,l,2-trichloro-l,2,2-trifluoroeth»ne
12) 1,1-dichloroethane
13) cis-l,2-dichloroethene
14) trichloromethane
15) 1,2-dichloroethane
16) 1,1,1-trichloroethane
17) benzene
18) carbon tetrachloride
19) 1,2-dichloropropane
20) trichloroethene
21) 2,2,4-triaethylpenUne
22) cis-l,3-dichloropropene
23) tr*ns-l,3,-dichloropropene
24) 1,1,2-trichloroethane
25) toluene
26) 1,2-dibroMefchane
27) tetrachloroethene
28) chlorobenzene
29) ethylbenzene
30) m+p-xylene
31) styrene
32) 1,1,2,2-Utraehlorotfcfwne
33) o-xylene
34) 4-ethylfcolucnt
35) l,3,5-tri«ethtjlb«nwne
36) l,2,4-tri«ethylbenzene
37) benzyl chloride
38) a-dichlorobenzene
39) p-dichlorobenzene
40) o-dichlorobenzene
41) 1,2,4-trichlorobenzene
42) hexachlorobutadiene
0.47
<0.10
<0.10
<0.10
<0.10
<0.10
0.47
<0.10
<0.10
<0.10
0.15
<0.10
<0.10
<0.10
<0.10
0.61
1.45
0.12
<0.10
<0.10
0.15
<0.10
<0.10
<0.10
3.40
<0.10
<0.10
<0.10
0.40
1.45
0.15
<0.10
0.47
0.15
0.12
0.38
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.44
0.58
<0.10
<0.10
<0.10
<0.10
0.44
<0.10
<0.10
<0.10
0.13
<0.10
<0.10
<0.10
<0.10
0.19
0.86
0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.20
<0.10
<0.10
<0.10
0.18
0.63
<0.10
<0.10
0.24
<0.10
<0.10
0.21
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.55
0.65
<0.10
<0.10
<0.10
<0.10
0.44
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.18
0.68
0.12
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.99
<0.10
<0.10
<0.10
0.15
0.56
<0.10
<0.10
0.19
<0.10
<0.10
0.19
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.31
0.46
<0.10
<0.10
<0.10
<0.10
0.50
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.16
0.50
0.12
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.61
<0.10
<0.10
<0.10
<0.10
0.30
<0.10
<0.10
<0.10
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.58
0.47
<0.10
<0.10
<0.10
<0.10
0.44
<0.10
<0.10
<0.10
0.10
<0.10
<0.10
<0.10
<0.10
0.77
1.23
0.12
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
2.98
<0.10
0.12
<0.10
0.43
1.49
<0.10
<0.10
0.52
0.13
0.13
0.41
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.49
0.43
<0.10
<0.10
<0.10
<0.10
0.49
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.32
1.17
0.12
<0.10
<0.10
0.13
<0.10
<0.10
<0.10
1.83
<0.10
<0.10
<0.10
0.24
0.93
0.25
<0.10
0.34
<0.10
<0.10
0.27
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.44
0.47
<0.10
<0.10
<0.10
<0.10
0.47
<0.10
<0.10
<0.10
0.13
<0.10
<0.10
<0.10
<0.10
0.30
0.93
0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
2.80
<0.10
<0.10
<0.10
0.43
1.46
<0.10
<0.10
0.43
<0.10
<0.10
0.25
<0.10
<0.10
<0.10
<0.10
<0. 10
<0.10
0.55
0.32
<0.10
<0.10
<0.10
<0.10
0.50
<0.10
0.38
<0.10
0.13
<0.10
<0.10
<0.10
<0.10
0.37
1.06
0.13
<0.10
<0.10
0.12
<0.10
<0.10
<0.10
1.98
<0.10
<0.10
<0.10
0.24
0.83
0.53
<0.10
0.32
0.10
0.10
0.25
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.52
0.40
<0.10
<0.10
<0.10
<0.10
0.47
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.53
1.61
0.12
<0.10
<0.10
0.18
<0.10
<0.10
<0.10
3.47
<0.10
0.12
<0.10
0.43
1.76
0.16
<0.10
0.62
0.18
0.18
0.52
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.44
0.28
<0.10
<0.10
<0.10
<0.10
0.47
<0.10
<0.10
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
0.24
1.00
0.13
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.43
<0.10
<0.10
<0.10
0.19
0.78
<0.10
<0.10
0.28
<0.10
<0.10
0.24
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.52
0.21
<0.10
<0.10
<0.10
<0.10
0.52
<0.10
0.24
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
0.53
1.48
0.12
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
3.29
<0.10
<0.10
<0.10
0.50
1.82
0.50
<0.10
0.61
0.16
0.16
0.47
<0.10
<0.10
<0.10
<0. 10
<0.10
<0.10
0.52
0.40
<0.10
<0.10
<0.10
<0.10
0.50
<0.10
<0.10
<0.10
0.13
<0.10
<0.10
<0.10
<0.10
0.19
0.46
0.12
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.53
<0.10
<0.10
<0.10
<0.10
0.28
<0.10
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
* Instrument Difficulties  in Resolving this Compound.
-------
    ORGflNICS LIST
                      COMPOUND
                                              LC0044   LC0018   LC0017   LC0074   LC0079   LC0064   LC0010   LC0073   LC0043   LC0057   LC0036   LC0028
                                               MORSE    MORSE   PSflPCfl   PSRPCfl    MORSE    MORSE   PSflPCfl   PSflPCfi    MORSE    MORSE   PSflPCR   PSRPCfl
                                              0748 HR  1920 HR  0730 HR  1845 HR  0720 HR   1920    0650 HR  1830 HR  0700 HR  1900 HR  0630 HR  1835 H
                                              1/06/90  1/06/90  1/06/90  1/06/90  1/07/90  1/07/90  1/07/90  1/07/90  1/08/90  1/08/90  1/08/90  1/08/9
o
CO
 1) dichlorodifluoromethane
 2) methyl chloride *
 3) l,2-dichloro-l,l,2,2-tetrafluoroethan*
 4) vinyl chloride
 5) nethyl bromide
 6) ethyl chloride
 7) trichlorofluoro*ethane
 8) 1,1-dichloroethene
 9) dichlorowethane
 10) 3-chloropropene
 11) l,l,2-trichloro-l,2,2-trifluoro*than*
 12) 1,1-dichloroethan*
 13) cis-l,2-dichloroethene
 14) trichloro«ethan*
 15) l,2-dichloroeth*ne
 16) 1,1,1-trichloroethan*
 17) benzene
 18) carbon tetrachloride
 19) 1,2-dichloropropan*
 20) trichloro*thene
 21) 2,2,4-tri»ethylp*ntan*
 22) cis-1,3-dichloropropen*
 23) trans-l,3,-dichloropropene
 24) 1,1,2-trichloroethan*
 25) toluene
 26) l,2-dibro«o*thar>*
 27) tetrachloroethene
 28) chlorobenzen*
 29) ethylbenzene
 30) «+p-xylene
 31) styrene
 32) l,l,2,2-t*trachloro*th«n*
 33) o-xylen*
 34) 4-*thyltolu*m
 35) l,3,5-tri«*lhylb*rtt*m
 36) l,2,4-tri*«thylb*nz*n*
 37) benzyl chloride
 38) «-dichlorobenzen*
39) p-dichlorobenzen*
40) o-dichlorobenzen*
41) 1,2,4-trichlorobenzen*
42) hexachlorobutadiene
0.53
0.38
<0.10
<0.10
<0.10
<0.10
0.50
<0.10
0.21
<0.10
<0. 10
<0.10
<0.10
<0.10
<0.10
0.31
2.06
0.11
<0.10
<0.10
0.21
<0.10
<0.10
<0.10
4.83
<0.10
<0.10
<0.10
0.86
3.12
<0.10
<0.10
1.04
0.20
0.20
0.58
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.43
0.25
<0.10
<0.10
<0.10
<0.10
0.44
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.16
0.30
0.12
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.44
<0.10
<0.10
<0.10
<0.10
0.18
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.53
0.89
<0.10
<0.10
<0.10
<0.10
0.47
<0.10
<0. 10
<0.10
0.13
<0.10
<0.10
<0.10
<0.10
0.44
0.96
0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.58
<0.10
<0.10
<0.10
0.25
0.87
0.18
<0.10
0.32
0.10
0.10
0.25
<0.10
<0.10
<0.10
<0.10
<0.10
<0. 10
0.41
0.35
<0.10
<0.10
<0.10
<0.10
0.44
<0.10
<0.10
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
0.12
0.44
0.12
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.53
<0.10
<0.10
<0.10
<0.10
0.30
<0.10
<0.10
0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.61
0.44
<0.10
<0.10
<0.10
<0.10
0.43
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.18
0.84
0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.02
<0.10
<0.10
<0.10
0.13
0.55
<0.10
<0.10
0.19
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.44
1.10
<0.10
<0.10
<0.10
<0.10
0.45
<0.10
<0.10
<0.10
0.12
<0.10
<0.10
0.11
<0.10
0.20
0.47
0.11
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<0.10
<0.10
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<0.10
0.62
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<0.10
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0.30
<0.10
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
<0.10
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<0.10
<0.10
<0.10
0.43
0.18
<0.10
<0.10
<0.10
<0.10
0.44
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
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0.19
0.87
0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.52
<0.10
<0.10
<0.10
<0.10
0.29
<0.10
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
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0.50
0.23
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<0.10
<0.10
<0.10
0.47
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
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0.21
0.48
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.21
<0.10
<0.10
<0.10
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0.30
0.99
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<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.99
0.72
<0.10
<0.10
<0.10
<0.10
0.45
<0.10
0.27
<0.10
0.11
<0.10
<0.10
<0.10
<0.10
0.74
2.61
0.12
<0.10
<0.10
0.32
<0.10
0.18
<0.10
6.32
<0.10
0.11
<0.10
0.99
3.60
0.50
<0.10
1.20
0.33
0.30
1.01
<0. 10 • ,
<0.10
<0.10
<0.10
<0.10
<0.10
0.59
0.38
<0.10
<0.10
<0.10
<0.10
0.49
<0.10
0.18
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
0.44
1.92
0.10
<0.10
<0.10
0.22
<0.10
<0.10
<0.10
3.50
<0.10
<0.10
<0.10
0.55
1.96
0.41
<0.10
0.65
0.16
0.19
0.56
<0.10
0.31
<0.10
0.21
0.21
<0.10
0.59
0.41
<0.10
<0.10
<0.10
<0.10
1.06
<0.10
0.22
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.43
1.28
0.12
<0.10
<0.10
0.13
<0.10
<0.10
<0.10
2.42
<0.10
<0.10
<0.10
0.35
1.27
0.61
<0. 10
0.44
0.13
0.12
0.35
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.5
<0.1
<0.1
<0.1
<0.1
<0.1
0.5
<0.1
0.3
<0.1
0.1
<0.1
<0.1'
<0.1
<0.1
0.3
1.3
0.1
<0.
<0.
0.
<0.
<0.
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2.7
<0.l
<0.1
<0.1
0.1
1.5
O.i
<0. 1
0.5
0.1
0.
0.
<0. I
<0.1
<0.
-------
                                           ORGflNICS LIST
                                                             COMPOUND
 u>
-8
1) dichlorodiflooro**th»ne
2) Mthyl chloride *
3) l,2-dichloro-l,l,2,2-tetr«fluoroeth«ne
4) vinyl chloride
5) .ethyl broaide
6) ethyl chloride
7) trichlorofluoroaethane
8) 1,1-dichloroethene
9) dichloro«eth«ne
10) 3-chloropropene
11) l,l,2-trichloro-l,2,2-trifluoroeth«ne
12) 1,1-dichloroethane
13) cis-l,2-dichloroethene
14) trichloroaethane
15) 1,2-dichloroefchane
16) l,l,l-trichloroeth«
17) benzene
18) carbon tetrachloride
19) 1,2-dichloropropane
20) trichloroethene
21) 2,2,4-tri«ethylpent«ne
22) cis-l,3-dichloropropene
23) trans-l,3,-dichloropropene
24) 1,1,2-trichloroethane
25) toluene
26) l,2-dibro«oeth«ne
27) tetrachloroethene
28) chlorobenzene
29) ethylbenzene
30) «+p-xylene
31) styrene
32) 1,1,2,2-tetrachloroethane
33) o-xylene
34) 4-ethyltoluene
35) 1,3,5-trinethylbenzene
36) 1,2,4-triaethylbenzene
37) benzyl chloride
38) o-dichlorobenzene
39) p-dichlorobenzene
40) o-dichlorobenzene
41) 1,2,4-trichlorobenzene
42) hexachlorobutadiene
OUP. DUP. DUP.
02154 BMI-14 LC0053
MORSE PSPPCfl HORSE
1919 HR 1850 HR 0706 HR
12/07/09 12/09/89 12/14/89
0.28
<0.10
<0.10
<0.10
<0.10
<0.10
0.71
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.42
0.97
0.14
<0.10
<0.10
0.14
<0.10
<0.10
<0.10
1.74
<0.10
<0.10
<0.10
0.28
0.99
<0.10
<0.10
0.37
<0.10
<0.10
0.28
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.73
<0.10
<0.10
<0.10
<0.10
<0.10
1.04
<0.10
0.40
<0.10
0.21
<0.10
<0.10
<0.10
<0.10
0.57
3.72
0.14
<0.10
<0.10
0.50
<0.10
<0.10
<0.10
6.21
<0.10
<0.10
<0.10
0.96
3.60
0.14
<0.10
1.27
0.35
0.33
0.97
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.08
<0.10
<0.10
<0.10
<0.10
<0.10
0.70
<0.10
0.64
<0.10
0.12
<0.10
<0.10
<0.10
<0.10
0.83
5.98
0.16
<0.10
<0.10
0.83
<0.10
<0.10
<0.10
14.38
<0.10
0.24
<0.10
2.50
9.56
0.76
<0.10
3.25
0.85
0.76
2.31
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
DUP.
LC0062
MORSE
0735 HR
1/02/90
0.43
0.59
<0.10
<0.10
<0.10
<0.10
0.59
<0.10
0.35
<0.10
0.19
<0.10
<0.10
<0.10
<0.10
0.87
3.42
0.12
<0.10
<0.10
0.46
<0.10
<0.10
<0.10
6.88
<0.10
0.10
<0.10
1.08
3.85
0.30
<0.10
1.31
0.35
0.34
1.02
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
DUP.
LC0036
PSflPCfl
0630 HR
1/08/90
0.66
0.52
<0.10
<0.10
<0.10
<0.10
1.33
<0.10
0.21
<0. 10
0.13
<0.10
<0.10
<0.10
<0.10
0.46
1.40
0.15
<0.10
<0.10
0.15
<0.10
<0.10
<0.10
2.72
<0.10
<0.10
<0.10
0.41
1.43
0.71
<0.10
0.50
0.12
0.13
0.40
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
                                           *  Instrument Difficulties in Resolving this Compound.
-------
U>
ORGflNICS LI5T

COMPOUND
1) dichlorodif luorooethane
2) *ethyl chloride *
3) l,2-dichloro-l,l,2,2-tetrafluoroethane
4) vinyl chloride
5) methyl bromide
6) ethyl chloride
7) trichlorof luoromethane
8) 1,1-dichloroethene
9) dichloromethane
10) 3-chloropropen*
11) 1, l,2-trichloro-l,2,2-trifluoroethane
12) 1,1-dichloroethane
13) cis-l,2-dichloroethene
14) trichloromethane
15) 1,2-dichloroethane
16) 1,1,1-trichloroethane
17) benzene
18) carbon tetrachloride
19) 1,2-dichloropropane
20) trichloroethen*
21) 2,2,4-trimethylpentane
22) cis-l,3-dichloropropen«
23) trans-l,3,-dichloropropene
24) 1,1,2-trichloroethane
25) toluene
26) l,2-dibromo«thane
27) tetrachloroethene
28) chlorobenzene
29) ethulbenzene
30) «+p-xylene
31) styrene
32) l,l,2,2-t«tr«chlarxwih«w
33) o-xylene
34) 4-ethyltoliMrw
35) 1,3,5-triMthtjlbanzww
36) l,2,4-tri«*tnylb«nz«m
37) benzyl chloride
38) m-dichlorobenzen*
39) p-di chlorobenzene
40) o-dichlorobenzen*
41) 1, 2,4-trichlorob*nzene
42) hexachlorobutadiene
RGX-003
PSflPCR
0727 HR
1/02/90
0.65
0.32
<0.10
<0.10
<0.10
<0.10
0.54
<0.10
<0.10
<0.10
0.25
<0.10
<0.10
<0.10
<0.10
0.24
1.95
<0.10
<0.10
<0.10
0.25
<0.10
<0.10
<0.10
3.67
<0.10
0.11
<0.10
0.57
1.20
0.40
<0.10
0.71
0.21
0.19
0.66
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
RXG-015
psflpcn
1959 HR
1/02/90
0.52
0.70
<0.10
<0.10
<0.10
<0.10
0.49
<0.10
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
<0.10
0.17
0.65
0.11
<0.10
0.21
<0.10
<0.10
<0.10
<0.10
0,82
<0.10
<0.10
<0.10
0.11
0.38
<0.10
<0.10
0.13
<0.10
<0.10
<0.10
<0.10
<0.10
<0. 10
<0.10
<0.10
<0.10
RGX-010
PSflPCfl
0740 HR
1/03/90
0.53
0.55
<0.10
<0.10
<0.10
<0.10
0.97
<0.10
<0.10
<0.10
0.14
<0.10
<0.10
<0.10
<0.10
0.18
0.64
0.11
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.00
<0.10
<0.10
<0.10
0.16
0.52
0.10
<0.10
0.18
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
RGX-014 I
PSflPCfl
0750
1/05/90
0.63
0.42
<0.10
<0.10
<0.10
<0.10
0.52
<0.10
0.21
<0.10
0.18
<0. 10
<0.10
<0.10
<0.10
0.52
1.39
0.10
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
2.87
<0.10
<0.10
<0.10
0.39
1.53
0.10
<0.10
0.50
0.14
0.11
0.42
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
RGX-R258
PSflPCfl
0700 HR
1/07/90
0.51
0.24
<0.10
<0.10
<0.10
<0.10
0.47
<0.10
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
<0.10
0.21
0.60
0.11
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.76
<0.10
<0.10
<0.10
0.11
0.36
<0.10
<0.10
0.11
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
RGX-004
PSflPCfl
1854 HR
1/08/90
0.62
0.37
<0.10
<0.10
<0.10
<0.10
0.59
<0.10
0.39
<0.10
0.25
<0.10
<0.10
<0.10
<0.10
0.46
1.39
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
2.65
<0.10
<0.10
<0.10
0.50
1.64
0.41
<0.10
0.59
<0.10
<0.10
0.34
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
DUP.
RGX-003
PSflPCfl
0727 HR
1/02/90
0.62
0.40
<0.10
<0.10
<0.10
<0.10
0.57
<0.10
0.11
<0.10
0.33
<0.10
<0.10
<0.10
<0.10
0.27
2.07
0.13
<0.10
<0.10
0.30
<0.10
<0.10
<0.10
3.89
<0.10
0.11
<0.10
0.62
2.14
0.46
<0.10
0.79
0.21
0.21
0.76
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
DUP.
RGX-015
PSflPCfl
1959 HR
1/02/90
0.54
0.46
<0.10
<0.10
<0.10
<0.10
0.52
<0.10
<0.10
<0.10
0.16
<0.10
<0.10
<0.10
<0.10
<0.10
0.68
0.11
<0.10
0.19
<0.10
<0.10
<0.10
<0.10
0.84
<0.10
<0.10
<0.10
0.13
0.40
<0.10
<0.10
0.14
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
OUP.
R6X-010
PSflPCfl
0740 HR
1/03/90
0.58
0.45
<0.10
<0.10
<0.10
<0.10
1.08
<0. 10
<0.10
<0.10
0.10
<0.10
<0.10
<0.10
<0.10
0.19
0.71
0.14
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
0.98
<0.10
<0.10
<0.10
0.16
0.52
<0.10
<0.10
0.19
<0.10
<0.10
0.18
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
OUP.
RGX-004
PSflPCfl
1854 HR
1/08/90
0.69
0.55
<0.10
<0.10
<0.10
<0.10
0.66
<0.10
0.43
<0.10
0.23
<0.10
<0.10
<0.10
<0.10
0.46
1.35
<0.10
<0.10
<0.10
0.14
<0.10
<0.10
<0.10
2.60
<0.10
<0.10
<0.10
0.41
1.64
0.34
<0.10
0.55
0.11
0.11
0.34
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
  * Instrument Difficulties  in Resolving this Compound.
-------
ORGANICS LIST
                  COMPOUND
                                                       DUP      DUP      OUP
 RUDIT    AUDIT    flUOIT    RUOIT    RUOIT    AUDIT    AUDIT    AUDIT    AUDIT
  CAN      CAN      CAN      CAN      CAN      CAN      CAN      CAN      CAN
BHI-031  BHI-041  BMI-026  BMI-032  BCL-043  BCL-034  BMI-041  BMI-026  Ba-043
1) dichlorodifluoroitethane
2) methyl chloride
3) l,2-dichloro-l,l,2,2-tetrafluoroethane
4) vinyl chloride
5) methyl bromide
6) ethyl chloride
?) trichlorofluoromethane
8) 1,1-dichloroethene
9) dichloroaethane
10) 3-chloropropene
11) l,l,2-trichloro-l,2,2-trifluoroethane
12) 1,1-dichloroeihane
13) cis-l,2-dichloroethene
14) trichloronethane
15) 1,2-dichloroethane
16) 1,1,1-trichloroethane
17) benzene
18) carbon tefcrachloride
19) 1,2-dichloropropane
20) trichloroethene
21) 2,2,4-trinethylpentane
22) cis-l,3-dichloropropene
23) trans-l,3,-dichloropropene
24) 1,1,2-trichloroethane
25) toluene
26) l,2-dibro*oethane
27) tetrachloroethene
28) chlorobenzene
29) ethylbenzene
30) m+p-xylene
31) styrene
32) 1,1,2,2-tetrachloroelhane
33) o-xylene
34) 4-ethyltoluen*
35) 1,3,5-triMthyllMnttrw
36) l,2,4-tri«ethylb»nzene
37) benzyl chloride
38) m-dichlorobenzene
39) p-dichlorobenzene
40) o-dichlorobenzene
41) 1,2,4-trichlorobenzene
42) hexachlorobutadiene
<0.10
<0.10
<0.10
1.26
5.82
<0.10
11.00
<0.10
1.80
<0.10
0.44
<0.10
<0.10
2.01
1.81
3.60
1.78
2.26
3.32
1.85
<0.10
<0.10
<0.10
<0.10
3.94
4.40
1.93
4.09
3.78
<0.10
<0.10
<0.10
4.11
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
3.70
12.06
<0.10
23.16
<0.10
3.54
<0.10
23.09
<0.10
<0.10
4.18
3.84
7.54
3.77
4.63
7.15
3.99
<0.10
<0.10
<0.10
<0.10
8.27
8.46
4.12
8.40
7.67
<0.10
<0.10
<0.10
8.38
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.79
5.61
<0.10
11.23
<0.10
1.72
<0.10
0.87
<0.10
<0.10
2.08
1.98
3.80
1.83
2.32
3.65
1.98
<0.10
<0.10
<0.10
<0.10
4.33
4.83
2.03
4.29
4.10
<0.10
<0.10
<0.10
4.49
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
4.69
11.44
<0.10
21.97
<0.10
3.37
<0.10
0.63
<0.10
<0.10
4.17
3.82
7.54
3.86
4.60
7.18
3.96
<0.10
<0.10
<0.10
<0.10
8.62
9.21
4.22
8.57
8.01
<0.10
<0.10
<0.10
8.87
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0. 10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
4.17
12.94
<0.10
23.05
<0.10
4.17
<0.10
23.92
<0.10
<0.10
4.38
4.03
7.54
4.11
4.63
7.81
4.07
<0.10
<0.10
<0.10
<0.10
8.96
8.79
4.10
8.82
8.05
<0.10
<0.10
<0.10
8.65
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
1.76
5.93
<0.10
11.03
<0.10
1.81
<0.10
0.87
<0.10
<0.10
2.15
1.99
3.83
2.12
2.28
3.62
2.02
<0.10
<0.10
<0.10
<0.10
4.81
4.98
2.09
4.66
4.33
<0.10
<0.10
<0.10
4.66
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
<0.10
-------
Appendix E-S. Meteorological Data Measured at the Alexander Avenue Site
Start
Date
12/5
12/5
12/6
12/6
12/7
12/7
12/8
12/8
12/9
12/9
12/10
12/10
12/11
12/11
12/12
12/12
12/13
12/13
12/14
12/14
12/15
12/15
1/2
1/2
1/3
1/3
1/4
1/4
1/5
1/5
1/6
1/6
1/7
1/7
1/8
1/8
U Theta So
m/s deg w/m2
1.14
1.07
0.13
0.16
1.2
1.9
3.56
2.75
1.52
1.02
1.24
0.92
1.03
1.27
0.77
0.41
0.41
1.31
0.95
1.26
1.33
1.56
1.34
1.54
3.67
2.24
2.99
0.65
3.39
2.68
1.21
4.32
3.92
1
1.58
1.01
156 81.1
164 0
235 43.7
73 -0.1
135 37.8
200 -0.1
216 42.7
177 -0.1
151 105.8
145 0
26 93.3
107 0
141 82.7
139 0
141 106.3
65 0
53 116.8
137 0
121 40.1
138 0
76 41.3
109 0
159 128.7
134 0
182 18.1
162 0
217 40.4
174 -0.1
191 19.9
172 -0.1
142 66.1
204 0
193 53.2
290 0
167 29.6
127 0
ppt
in
0.01
0
0.01
0
0.13
0.42
0.1
0
0
0
0
0
0
0
0
0.01
0
0
0
0
0
0
0
0
0.06
0.26
0.02
0.08
0.47
0.11
0.21
0.9
0.16
0.52
0.55
1.97
n
%
0
0
17
10
0
1
0
0
0
0
31
2
0
0
3
17
33
1
3
0
3
0
0
0
0
0
0
1
0
0
0
0
0
30
2
1
ne
%
0
4
13
4
1
0
0
0
1
0
23
27
2
0
9
20
10
1
11
0
44
2
1
1
0
0
0
1
0
0
3
0
0
12
5
4
e
%
3
6
8
20
16
1
0
1
8
6
11
8
10
7
12
15
6
13
12
13
17
59
7
13
0
0
1
12
3
0
8
0
0
5
13
24
se
%
57
35
17
17
60
15
3
34
51
65
22
47
65
76
42
29
19
70
68
72
24
34
50
72
25
38
3
38
22
42
53
26
13
12
33
51
s
%
23
44
17
4
15
39
33
53
32
28
3
14
16
15
26
5
23
15
6
15
13
4
40
13
61
60
28
6
56
56
15
22
58
6
39
7
sw
%
5
3
10
4
8
35
48
13
6
1
2
1
6
2
4
1
6
0
0
0
0
1
3
1
14
0
47
8
14
3
11
41
29
24
8
4
w
%
6
4
8
18
1
3
16
0
2
0
6
1
1
0
1
3
1
0
1
0
0
0
0
0
0
1
19
26
6
0
3
11
0
3
0
5
nw <
%
7
2
10
22
0
6
0
0
0
0
2
1
0
0
3
9
3
0
0
0
0
0
0
1
0
0
1
7
0
0
6
0
0
8
0
3
Im/s
%
26
32
23
48
38
6
0
3
13
44
21
24
31
28
38
61
24
22
32
20
15
13
24
13
0
2
3
17
9
1
29
0
1
2
14
37
Average:  1.62   151  31.9  0.17    4
39    25   10
20
U = wind speed; Theta = wind direction (degrees from north); So = solar insolation; ppt =
precipitation.
                                         313
-------
Appendix E-6.  Linear Correlations Between Sites
                                        315
-------
 Appendix E-6(a).  Concentration of Fine-Particle Mass at the Morse Supply Site Versus

 the Alexander Avenue Site.  The 1;1 line is drawn on the graph.	
1

I
0)


iZ
-------
 Appendix E-6(b). Concentration of Fine-Particle Organic Carbon at the Morse Supply Site
 versus the Alexander Avenue Site. The 1:1 line is drawn on the graph.        	
 I
S
 CO
O
 o

 CO
 D)

O
 (D
CD
(0
      15
      10
       0
        0
10
20
30
40
                    Alexander Avenue Site Organic Carbon, Mg/m3
                                    318
-------
Appendix E-6(c). Concentration of Fine-Particle Sulfur (measured by x-ray fluorescence)
at the Morse Supply Site versus the Alexander Avenue Site. The 1:1 line is drawn on the
graph.	
   3000
        0
500
1000
1500
2000
2500
3000
                        Alexander Avenue Site Sulfur,
                                    319
-------
   Appendix E-6(d). Concentration of Fine-Particle Lead (Pb) at the Morse Supply Sites
   versus the Alexander Avenue Site. The 1;1 line is drawn on the graph.	
f>

I

73
CTJ
CO

0)
CO
       40
       20
         0
          0
20
40
60
80
100
                      Alexander Avenue Site Lead,
                                       320
-------
Appendix E-6(e). Sulfate (measured by ion chromatography) versus Sulfur (measured by

x-ray fluorescence).  The 3:1 line is drawn on the graph.	
fi
S=
a
CO

o
      0
       0.0
0.5
1.0
1.5
2.0
                a


           ALEXANDER

           SITE

                 *

           MORSE

           SITE
                                XRF Sulfur,
              Slope = 2.47

              Intercept = 0.06

              r = 0.97
2.5
3.0
                                     321
-------
Appendix E-7.  PAH Results
                                     323
-------
         technology |
                              NSI Technology Services Corporation
                                                          A Subsidiary of
                                                 MenTech International Corporation
                                                    Environmental Sciences
                                                  P.O. Box 12313,2 Triangle Drive
                                                  RMearch Triangle Park, NC 27709
                                                     Telephone (919) 549-0611

NEMO

Date:     27-March-90

To:  W. Ellenson

From:  R. S. Whiton/

Subject:  Puget Sound  Samples


My GC/MS analysis  of the Puget Sound filter extracts is  complete.
Preliminary analysis of the ImL extracts showed that they were
too dilute and the samples were therefore transferred to conical-
bottomed vials and concentrated to approximately lOOuL under
streams of nitrogen.   Five samples (sets 1, 2, 4, 5, and 7) were
analyzed by full scan  GC/MS using a HP 5970 MSD with the
following conditions:

     column: HP Ultra2, 25m x 0.20mm, O.llum film, + 1m  retention
               gap,  35cm/s He carrier
     injection: IfiL cool on-column
     column temp:  40*C(lmin), 15°C/min to 200°C(Omin), 3°C/min to
               310°C(10min)
     MS: scanned 50-400 arou, 1.2 scans/s

The total ion chromatograms are attached as figures 1-5  and the
peak identifications are contained in tables 1-5.  All
identifications are based on automated searches of mass  spectral
libraries and should be considered tentative identifications.

All seven samples  were analyzed by selected ion monitoring (SIM)
GC/MS  for detection of PAH and retene.  The chromatographic
conditions were the same as given above, and the SIM parameters
were:
     5-11 min- m/z 128, 152, 154, 166; 75ms each
     11-19 min- m/z 178, 202, 219, 234; 75ms each
     19-40 min- m/z 228, 252, 276, 278; 75ms each
     40-50 min- m/z 300 for 200ms

The results are contained in table 6.  The quantities determined
should be taken as not better than +/- 50%, and the qualitative
identifications are somewhat uncertain due the constant  loss  of
chromatographic performance caused by the high levels of non-
volatile material  in the extracts.  The results for sets 4 and 5
were particularely poor, and most of the PAHs may have been
missed due to interferences or shifting retention times.
-------
The difficulty of the analysis was compounded by the fact that
the levels of PAH were near the detection limits of the
instrument.  If five to ten times more air were to be sampled, it
could be possible to clean up the samples and get more accurate
data.
-------
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-------
Table 1.  Peak identifications for Set 7.

Peak #          Identification

1         2-Chlorocyclohexane
2         Dichlorocyclohexane
3         Dichloromethylbenzene
4         Benzoic acid
5         Chloro(2-chloroethyl)benzene
6         Cyclododecane
7         Hexadecanoic acid
8         Octadecanoic acid
9         Phthalate ester

Many of the unidentified peaks in the range of 5-10 minutes
appear to be chlorine containing compounds, many with apparent
benzyl structures.
                                337
-------
Table 2.  Peak identifications for Set 1.

Peak #         Identification
1
2
3
Dibutyl phthalate
Butylbenzyl phthalate
possible match to di-lauryl-thio-di-propionate?
Table 3.  Peak identifications for Set 2.

Peak #         Identification
1
2
3
4
Dibutyl phthalate
Substituted alkane- alcohol or alkene?
Phthalate ester
possibly Octahydro-phenanthrenecarboxylic acid?
Table 4.  Peak identifications for Set 4.

Peak #         Identification
1
2
3
4
5
Dibutyl phthalate
Butyl,benzyl phthalate
Chrysene/benz(a)anthracene
Bis(2-ethylhexyl) phthalate
possibly Di-lauryl-thio-di-propionate?
Table 5.  Peak identifications for Set 5.

Peak #         Identification
1
2
3
4
5
6
Dibutyl phthalate
Butyl,benzyl phthalate
Chrysene/benz(a)anthracene
Bis(2-ethylhexyl) phthalate
PAH of molecular weight 252
possibly Di-lauryl-thio-di-propionate?
A = alkanes
* = peak contained in blank  (set 7)
                               338
-------
Table 6.  Results of Selected Ion Monitoring (SIM) Analysis for Fine-Particle PAH Compounds

                                                ng per Sample Set***
Compound
Naphthalene
Acenaphthylene
Acenaphthene
Fluorene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benzo(a)anthracene
Chrysene
Total Benzofluoranthenes
*Benzo(e)pyrene
Benzo(a)pyrene
Indeno(l,2,3-c,d)pyrene
Dibenzo(a,h)anthracence
Benzo(g , h , i)perylene
**Coronene
Set
1
1.8
-
-
-
5.2
2.7
23
34
28
59
56
50
51?
50
+
85
+
Set
2
1.6
-
-
-
nq-I
nq-I
68
83
nq-I
nq-I
160
140?
140?
130?
26?
210?
+
Set
3
1.9
-
4.3
-
4.6
-
18
25
18
51
50
48
35
50
?
82
+
Set
4
+
-
-
-
4.8
2.7
25
34
23
82
47
38?
23?
25?
+
+
+
Set
5
5.5
-
7
-
21
?
160
130
-
-
-
-
+
-
-
-
+
Set
6
+
-
-
-
14
14
95
88
-
-
-
?
7
-
-
-
+
Set
7
+
-
-
-
3.5
3.7
-
-
-
-
-
-
-
-
-
-
-
#Retene                       60,482 198,660 72,774  56,774 135,568 57,192
 +     Identified but below quantitation limits.
 ?      Uncertain ID due to retention time shifts.
 nq-I   Not quantitated due to interfering peak(s).
 *      B(e)P estimated from  B(a)P calibration.
 **     Coronene not quantitated.
 #      Retene numbers are peak areas-quantitation standard not available.
 ***   Set 1 =  Morse Supply site, December, Hogged fuel up
       Set 2 =  Morse Supply site, December, Hogged fuel down
       Set 3 =  Morse Supply site, January, Hogged fuel up
       Set 4 =  Alexander Avenue site, December, Hogged fuel up
       Set 5 =  Alexander Avenue site, December, Hogged fuel down
       Set 6 =  Alexander Avenue site, January, Hogged fuel up
       Set 7 =  Eight field blanks.
                                         339
-------
Appendix F.  Diffusion/Transport Modeling
      F-l.   WV3 Eulerian Grid Dispersion Model	343
      F-2   Model Input - Source Emissions	345
      F-3.   Model Input - Meteorological Vertical Eddy Diffusivities	351
      F-4.   Model Input - Sampling Intervals  	355
      F-5.   Model Output - Simulations  	357
      F-6.   Development of the Mobilization Coefficient Model and
            Results for the Tacoma Tideflats  	369
                                     341
-------
Appendix F-l.  WV3 Eulerian Grid Dispersion Model
A mathematical model was developed to simulate the emission, dispersion, and deposition of
toxic contaminants, through the atmosphere and into the watershed of Commencement Bay.
The governing equation expresses conservation of mass:

             dC/dt =  - Grad [U-C] + Sources - Sinks.                              [1]

In  [1],  the first  term to the right of  the  equality  accounts  for  transport,  the second  for
emissions,  and the third for depositions or chemical degradation.  C is the local concentration
of a specified tracer, and U is the local wind velocity, both specified as functions of time and
space.  In Cartesian coordinates, the Grad operator is d/dx + d/dy +  d/dz.

It is not straightforward to solve equation [1], because the U«C term displays complex structure
over a wide span of scales, both in space and time.  A common approach is to approximate the
transport term as:

- Grad [U.C] = - [U dC/dx + V dC/dy + W dC/dz] + [Kx Cxx + Ky Cyy  + Kz Czz].[2]

In [2], U,  V, and W are three components of the winds, averaged over a specified time,  T0.
Cxx, Cyy, and Cxx are the second spatial derivatives [the curvatures] in the three Cartesian
coordinates (x,y,z), also averaged over T0.  Kx, Ky, and Kz are semi-empirical "diffusivity"
coefficients that can be obtained from measurements of the variability of U, V, and W over
times that are shorter than T0.  The averaging time, T0, is usually taken as the interval between
reported measurements of U and V,  typically an hour.   The vertical velocities, W,  are
approximately zero close to the ground.

The Source terms in [1] must be externally specified. For mathematical convenience the Sink
term is usually approximated as linearly proportional to C:

              Sink =  Vs • C.                                                        [3]

The coefficient Vs, is called a "deposition velocity".  The deposition velocity is defined as
follows:

              Vs  = Kz . V1 • 0.                                                     [4]

In  equation [4],  Kz represents  eddy  diffusivity.  X"1 is the roughness length and 0 is  the
"sticking"  fraction.  Thus, the velocity of deposition depends on transport (eddy diffusivity),
the character of the surface  (roughness  length), and the tendency of the particle  to remain
(sticking fraction).

Equations [1] to [3] can be solved analytically only for point sources in the steady state, with
constant Kx, Ky, Kz,  and Vs,  and with uniform boundary conditions. This approach yields
"Gaussian Plumes", a common approximation that is widely and sensibly used for reasonably
steady winds in simple terrain.

When winds are  light and variable, however,  and when  the  terrain  is complexly bounded,
Gaussian Plumes  become progressively unrealistic. With the advent of microprocessing, both
with increasingly powerful table-top computers and with instrumentation to  record and store
wind information sampled at shorter intervals [T0 = minutes  or  seconds, instead  of tens of
minutes], it is now practical to attempt explicit numerical integration  of equations  [1] to  [3].
One model to do this is "WYNDvalley".


                                          343
-------
WYNDvalley, version 3.01 (hereafter WV3), is a time-dependent Eulerian grid simulation that
integrates equations [1] to [3] in three dimensions with arbitrarily varying emissions, both in
time and space.  The model permits flexible boundary  conditions and the separation of the
deposition velocity, Vs,  into steady  and time-varying components,  as  with rain-modulated
removal of soluble contaminants.

WV3 (and earlier versions) have been compared with observations and with predictions from
RAM, a standard  Gaussian  Plume model,  for PMW at  six sites in the Pacific Northwest,
including data from 1985 and 1986 at Fire Station No.  12 in the Tacoma Tidefiats. The earlier
version of WV3  proved superior to RAM in five out of six scoring criteria which depend on
matching observations with simulations, both in time and space. For the sixth, neither model
was  superior  to the other  (Harrison et al., 1990).

One of these  scoring criteria, the mean relative error (MRE) is defined as:

       MRE  = sqr {< (2-[ O  P ] / [O + P])2 >}.                                   [5]

In equation [5] the < brackets > denote averages over the sets observations, O and predictions,
P. WV3 displayed MRE scores of about 30 percent at Fire Station No. 12 with data from more
than 400 days, including a week of severe stagnation weather during December of 1985.
                                         344
-------
Appendix F-2. Model Input - Source Emissions
PMIO and TSP
Appendix F-2(a) summarizes the point sources of PM10 in the Tacoma Tideflats that emit one
or more kilograms per day, as compiled by the Puget Sound Air Pollution Control Agency
(PSAPCA) for  1988. The first two columns in this table give X and Y coordinates of each
source in UTM (kilometers).  The third column lists the estimated PM10 emissions (kg/day).
The 4th and 5th columns code the emission heights (1  denotes 0-66 meters;  2 denotes >  66
meters).  Numbers preceded by a forward slash (/) are PSAPCA registries. Numbers preceded
by a back slash (\) refer to source-profiles that will be discussed  below.

The numbers in Appendices  F-2(a) and F-2(b) refer to particles of diameters equal to 10
microns or less.  The PS-1 instrument used in the present study to collect the "total" suspended
particles (PM^^) admit particles of larger diameters than 10 microns: hence all the numbers
above do not strictly correspond to what was collected in the aerosol samples.
The present study is not primarily concerned with either PM10 or PM^j,, except as a route to
estimate the emissions of specific toxic contaminants, with especial attention given to Cu, Zn,
As, Pb, and a variety of polyaromatic hydrocarbons (PAH).  To estimate the emissions of these
contaminants, we have sought source "profiles" with measurements of the weight fractions of
various contaminants contained in filter  samples collected for a variety of source types, and
assigned a source-type profile to  each point source of Appendix F-2(a) and area source of
Appendix F-2(b).

Appendix F-2(c) contains profiles for the Cu, Zn, As, and Pb, and Appendix F-2(d) for several
PAHs.

Entries in Appendix F-2(c) are given as percent by mass in the TSP mode, where available.
PM10 or Coarse-Particle if not.  Profile numbers not beginning with 0000# derive from Core
(1989).  Others derive from Larson and Kalman, Hopke, the STAGS study, or the Simpson
source profile study performed for this project.
                                         345
-------
Appendix F-2(a).  Diffusion/Transport Model Input - Point Sources
TACOMA PM10 (1988)
xutm yutm kg/day
546.
546.
546.
55
55
50
546.50
542.
545.
545.
546.
546.
20
60
60
00
00
547.80
547.85
547.60
542.90
542.95
542.
543.
543.
543.
543.
543.
543.
543.
543.
543.
543.
547.
547.
547.
545.
545.
545.
545.
545.
545.
545.
547.
546.
542.
545.
544.
546.
547.
542.

547.

547.

90
50
50
50
50
50
50
50
40
40
40
10
10
10
90
90
90
90
90
90
90
70
55
25
65
42
10
10
90

65

85

5235
5235
5235
5235
5234
5235
5235
5235
5235
5234
5234
5233
5234
5234
5234
5234
5234
5234
5234
5234
5234
5234
5234
5234
5234
5235
5235
5235
5233
5233
5233
5233
5233
5233
5233
5235
5235
5234
5235
5235
5235
5235
5232

5234

5234

.45
.50
.65
.60
.65
.30
.25
.00
.05
.20
.05
.90
.25
.25
.20
.70
.70
.70
.60
.60
.60
.60
.80
.80
.80
.20
.20
.20
.50
.50
.50
.50
.50
.50
.50
.50
.45
.65
.20
.13
.00
.60
.70

.15

.15

4.2
72.0
14.0
7.0
32.9
35.5
9.9
11.5
3.5
3.9
3.9
5.2
26.3
12.0
46.6
14.0
1054.0
140.0
228.0
84.0
524.0
28.0
195.0
30.0
30.0
1.7
18.9
8.9
18.2
7.9
7.9
3.7
11.7
3.7
16.3
3.1
7.4
30.4
24.2
22.2
31.0
49.3
28.0

209.1

313.6

Source
levl sked
1
1
1
1
1
1
1
1
1
1
1
1
2
1
1
2
2
2
2
2
2
2
2
2
2
1
1
1
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1

2

2

1 , Buffelen
1 , Buffelen
1 , Buffelen
1 , Buffelen
1 , Cont. Grain
1 , Cont. Lime
1 , Cont. Lime
1 , Domtar Gyp.
1 , Domtar Gyp.
1 , Kaiser
1 , Kaiser
1 , Kaiser
1 , Puget S. Ply.
1 Puget S. Ply.
1 Puget S. Ply.
1 Simpson
1 Simpson
1 Simpson
1 Simpson
1 , Simpson
1 , Simpson
1 , Simpson
1 , Simpson
1 Simpson
1
1
1
1
1
1
1
1
1
1
1
1
1
4
4
4
4
1
1
Simpson
USG Interiors
USG Interiors
USG Interiors
US Oil
US Oil
US Oil
US Oil
US Oil
US Oil
US Oil
Woodworth
Buffelen
Cont. Grain
Cont. Lime
Tacoma Port
Dombar Gyp.
Gen. Metals
Scofield

1 , Kaiser

1 , Kaiser

Reg.#
/ 10340
/10340
/ 10340
/ 10340
/21430
/11820
/I 1820
/10016
/10016
/13461
/13461
/13461
/ 11974
/I 1974
/I 1974
/12317
/12317
/12317
/12317
/12317
/12317
/12317
/12317
/12317
/12317
/12609
/12609
/ 12609
/12593
/12593
/12593
/12593
/12593
/12593
/12593
/16043
/ 10340
/21430
/I 1820
/ 10074
/10016
/21432
/10895

/13461

/13461

Code
\22302
\12706
\22203
\22203
\21401
\23202
\22203
\12707
\27601
\3122
\3122
\3122
\12706
\22302
\22203
\00009
\00007
\00009
\00008
\00008
\00009
\00009
\00009
\00009
\00009
\12707
\28202
\22203
\13502
\13502
\13502
\13502
\13502
\3132
\13502
\3112
\22302
\21401
\23202
\00012
\27601
\3193
\51
\3111
\3173
\29102
\3173
\29102
Comments
dryer
boiler-wood
baghouse
cyclones
baghouse
kiln and hydrator
baghouse
plywood drier kiln
baghouse
dry scrubbers
dry scrubbers
dry scrubbers
boiler-wood
dryer
baghouse
boiler#l oil
boilers#2-5 wood
boiler#6 oil
kiln#l oil
kiln#2 oil
rcvryboiler#3resOil
smelt. tank#3
rcvryboiler#4resOil
smelt. tank#4east
smelt. tank#4west
plywood oven
cupolas
filters
h8-ll resOil
h201 + nat gas
h3 + process
h901 gas
hi 102-4 801a-c "
asphalt heaters "
boilers 4&5
scrubber
dryers
J

marine cargo handling



roof monitor

roof monitor

                                       346
-------
Appendix F-2(a). Point Sources (cont'd)
TACOMA PM10 (1988)
xutm yutm kg/day
547.

547.

548.
542.
547.

543.
546.

537.
546.

542.
540.

546.
548.
65

85

20
95
70

22
55

55
55

98
00

80
00
5233

5233

5234
5234
5235

5233
5235

5229
5233

5232
.90

.90

.20
.25
.50

.60
.95

.65
.10

.38
5230.95

5232

.50
5234.70
137

209

.2

.1

71.0
23.9
127

.4

44.3
9.

3.
3.

2.
195

5.
5

5
2

5
.0

0
22.0
Source
levl sked
2

2

1
1
1

1
1

1
1

1
1

1
1
1 ,

1 ,

1 ,
1 ,
4 ,

4 ,
1 ,

1 ,
4 ,

4 ,
4 ,

4 ,
4 ,
Kaiser

Kaiser

Lone Star
Puget S. Ply.
Woodworth

Coastcraft
Sound Refng.

Pac. Intnl.
Lianga

Harmon
W. Coast Door

Sierra Sandbl.
Tacoma Boat
Reg.#
/13461

/13461

/14071
/I 1974
/16043

/10463
/13828

/ 12050
/13511

/10995
/12716

/10068
/12429
Code
\3173
\29102
\3173
\39102
\51
\22302
\3112
\3111
\22203
\3132
\13502
\51
\12706
\22203
\22203
\22203
\12706
\51
\00013
Comments
roof monitor

roof monitor


dryers













Total =
4,286 kg/day
Appendix F-2(b).  Diffusion /Transport Model Input - Area Sources
                   Type
                         Annual Average
                      Emissions (kg/day)
                   Woodsmoke

                   Gas/Diesel:

                   Vehicle exhaust
                   Resuspended soil and road dust
                   Ships
                   Railroads
                                    109
                                    211
                                   1049
                                     19
                                     18

                                  1,406
                                         347
-------
Appendix F-2(c). Source Apportionment Data  Cu, Zn. As. Pb
Entries are weight percent.
Profile ID     Cu       Zn
As
Pb
Comment
12706
12707
13502
21401
22203
23104
23202
25403
27601
28202
3324
314
3111
3112
3132
3173
3193
51
22302
00001
00002
00003
00004
00005
00006
00007
00008
00009
00011
00012
00013
.068
.007
.002
.05
.018
.002
.006
.005
.002
.260
.078
.117
.006
.026
.110
.076
.990
.000
.000
.098
.018
.002
.024
.739
.418
.049
.013
.006
.051
.060
.005
.481
.063
.002
.000
.008
.002
.013
.000
.009
.830
.006
.200
.006
.043
.018
.010
.870
.003
.000
.193
.030
.010
.020
.230
.212
.607
.008
.037
.260
.120
.000
.019
.005
.001
.000
.000
.002
.005
.000
.004
.013
.018
.000
.000
.000
.000
.000
.000
.000
.000
.020
.000
.000
.000
.000
.010
.032
.001
.003
.005
.030
.000
.039
.019
.000
.000
.000
.001
.023
.000
.006
.230
.053
.000
.003
.020
.349
.042
.050
.000
.000
.465
.021
.005
11.6
.035
.250
.262
.485
.000
.150
.130
1.2
hogged fuel boiler
hogged fuel boiler
residual oil boiler
grain elevator
wood sander dust
recovery furnace
lime kiln
paint spray booth
gypsum
cast iron cupola
aluminum potline
natural gas boiler
rock crusher
asphalt batch plant
distillate oil furnace
alumina fugitives
car shredder
cement dust fugitives
veneer dryer
freeway air (Larson)
generic soil (Hopke)
woodstove (Larson)
autoexhaust (Hopke 1985)
diesel (Hopke 1985)
50:50 diesel: freeway air
hog fuel Simpson (NEA)
lime kiln Simpson (NEA)
recovery boil Simpson (NEA)
STAGS Tideflats soil
STAGS road dust
Tacoma Boat
                                       348
-------
Appendix F-2(d). Source Apportionment Data/Polyaromatic Hydrocarbons	

Entries are PPM by mass in the PM^ mode.

ID    FLOR  PHEN  ANTH  FLUO  PYRE   CHRY  BAP    RETE  COMMENT
12317
12317
12706
13502
23104
00001
00003
00005
00006
0.
0.
0.43
0.43
0.44
-999.
550.
0.26
0.26
7.
0.
3.53
0.41
5.05
231.
1148.
5.2
118.
3.5
0.
3.28
0.41
5.00
60.
710.
0.50
30.
18.
23.
2.24
8.38
3.15
1453.
432.
• 9.4
220.
16
0
6
11
4
2560
308
10
1485


.48
.60
.65
.
.
.2
.
4.9
0.
2.42
0.41
2.85
659.
196.
2.00
330.
5.6
0.
0.54
0.41
0.79
274.
74.
0.80
137.
26.
18.
39.
63.
23.
-999.
-999.
-999.
-999.


6
8
9




hogged fuel
recvry fur
hogged fuel
resid oil
recvry fur
autos
woodstove
diesel
"vehicles"
Lines 1 - 2 are from PSAPCA report for Simpson.
Lines 3 - 5 are from John Core.
Lines 6 - 8 are from Larson.
Line 9 is a 50:50 composite of autos -Hdiesels.
Abbreviations are:

            FLOR  fluorene
            PHEN  phenanthrene
            ANTH  anthracene
            FLUO  fluoranthene

Missing entries are flagged by -999.
PYRE  pyrene
CHRY  chrysene
BAP   benzo(a)pyrene
RETE  retene
                                      349
-------
Appendix F-3. Model Input - Meteorology, Eddy Diffusivities


A portable meteorological station collected data at the Alexander Avenue (PSAPCA) site in the
Tacoma Tideflats between July 6th, 1989 and January 9th, 1990.

These data were recorded in 27 files containing 2.2 Mbytes when stored in simple ASCII and about
0.95 MBytes in compressed binary.

These data may be unpacked and presented in various ways.  In one of these the first few lines are:
day
PST
hrs
U
m/s
theta
deg
SigU
m/s
U(SigT)
m/s
dT/dz
deg/m
S
w/m2
PPT
in
P G T W
187    1700   3.84    339.9     0.947   0.896      -.2498    409.6    0.00    2
187    1705   4.60    346.1     1.049   1.188      -.2498    409.6    0.00    2

Here U and theta are the wind velocity and direction, averaged over five-minute intervals.  SigU
is the  standard deviation in the velocity, measured at one second intervals and averaged over
five-minutes.  U(SigT) is the product of the five-minute averaged U times the five-min averaged
one-second  standard deviations of theta.  (Comparisons of SigU with U(SigT)  reveal that  the
horizontal eddies in wind velocity and direction are essentially isotropic.) dT/dZ is the temperature
gradient between two and 10 meters; S is the solar insolation, PPT the increment of rain during
the preceding five minutes, and PGTW is a Pasquill-Gifford-Turner-Wilson stability classes, derived
from the insolation and the temperature gradients.
                                           351
-------
Appendix F-3(a).  Vertical Eddy-Diffusivities through Monin-Obukhov Similarities
Z = 50 meters
Zm = 4.47 meters
Zo = 0.25 meters
T = 283 degK
-U(m/s)--> 0.50
dT/dZ + 0.01
-0.0250
-0.0225
-0.0200
-0.0175


4.59*
4.49*
4.38*
4.26*
-0.0150 4.13*
-0.0125 3.99*
-0.0100 3.82*
-0.0075 3.64*
-0.0050 2.98
-0.0025 1.88
-0.0000 0.83
0.0025
0.0050
0.0075
0.0100
0.0125
0.0150
0.0175
0.0200
0.0225
0.0250
0.39
0.22
0.13
0.07
0.05*
0.03*
0.03*
0.03*
0.03*
0.03*
1.00
entries below
7.00
6.48
5.95
5.42
4.87
4.32
3.76
3.20
2.66
2.15
1.66
1.33
1.09
0.91
0.78
0.67
0.58
0.51
0.45
0.39
0.34
1.50
are Kz (n
6.01
5.64
5.27
4.89
4.53
4.16
3.81
3.47
3.14
2.84
2.49
2.28
2.05
1.86
1.70
1.57
1.45
1.35
1.25
1.17
1.09
2.00
2/ x
1 /SJ 	 .
5.85
5.58
5.31
5.05
4.79
4.54
4.29
4.06
3.84
3.63
3.32
3.20
3.00
2.82
2.67
2.53
2.40
2.28
2.18
2.08
1.99
2.50
>
6.12
5.91
5.71
5.51
5.32
5.13
4.95
4.77
4.60
4.44
4.15
4.09
3.92
3.76
3.62
3.49
3.36
3.25
3.14
3.04
2.94
3.00

6.60
6.44
6.28
6.13
5.98
5.83
5.68
5.54
5.40
5.27
4.98
4.98
4.83
4.69
4.56
4.43
4.31
4.20
4.10
4.00
3.90
3.50

7.21
7.08
6.95
6.82
6.70
6.58
6.45
6.34
6.22
6.11
5.82
5.86
5.73
5.60
5.48
5.37
5.26
5.15
5.05
4.95
4.86
For entries marked with (*) Z >  j Lm |, which is not physically possible.
                                          352
-------
Appendix F-3(b).   Horizontal Eddy Diffusivities, Kxy, Plotted as  a Scattergram  Against

Horizontal Wind Speeds	
                  2.0
                      <—U  Sipia(Theta) (n/s)
                  1.5
                  1.0-

                            -v '^ ••Vi.tU ->v* £\t$ZM\**\'m\' v\"J'"j./v*''-"."'/
                  0.5
                                 «               :-_

                                 nrailMk/VJ /^vr!f *y ' vk*. ."-j


                                        r!r'. r> •'.*••
                                        '  *•  •
                  0.0
                     0
2  —  U (n/s) —>  5
8
                                              353
-------
Appendix F-3(c). Scattergram of the Transverse and Longitudinal Components of Horizontal
Eddy Variances	                              	
               2.8
               1.5
               1.0
               8.5
               8.8
                    <— U Signa(Theta)  (n/s)
                  8
8.5
                                  — Signa (U)   (n/s)
1.8
1.5
2.8
                                        354
-------
Appendix F-4.  Model Input - Sampling Intervals
Code
AS0724,
AS0727,
AS0803,
AS0814,
AS0821,
AS0824,
AS0828,
AS0907,
AS0911,
AS0914,
AS0918,
AS 1102,
AS 1109,
AS1113,
AS 1127,
AS 1130,
AS 1204,
AS 1207,
AS1211,
AS1214,
AS1218,
AS0102,
MS0727,
MS0814,
MS0821,
MS1116,
MS1211,
MS1214,
SL0727,
SLOSH,
SL0821,
SL1116,
SL1211,
TM0727,
TM0814,
TM0821,
TM1211,
TM1214,
RS0727,
RS0814
RS0821,
RSI 116,
RSI 127,
RS1211,
RS1214,
Start
Mo Da Hr
7
7
8
8
8
8
8
9
9
9
9
11
11
11
11
11
12
12
12
12
12
1
7
8
8
11
12
12
7
8
8
11
12
7
8
8
12
12
7
8
8
11
11
12
12
24
27
3
14
21
24
28
7
11
14
18
2
9
13
27
30
4
7
11
14
18
2
27
14
21
16
11
14
27
14
21
16
11
27
14
21
11
14
27
14
21
16
27
11
14
16
19
17
14
14
10
12
14
9
8
14
21
8
19
14
00
22
8
20
21
18
18
15
12
13
15
15
14
14
12
13
17
15
18
13
14
16
16
12
11
12
16
13
14
8
Stop
Mo Da
7
7
8
8
8
8
9
9
9
9
9
11
11
11
11
12
12
12
12
12
12
15
7
8
8
11
12
12
7
8
8
11
12
7
8
8
12
12
7
8
8
11
11
12
12
27
31
10
17
24
28
1
11
14
18
21
6
13
16
30
4
7
11
12
15
21
16
31
17
24
20
12
15
31
17
24
20
12
31
17
24
12
15
31
17
24
20
30
12
15
Hr
19
16
17
13
10
12
10
9
8
14
21
19
19
20
00
21
7
20
20
15
17
12
12
11
9
12
16
16
13
12
10
12
15
15
17
11
16
16
12
11
9
12
8
16
16
                                       355
-------
Appendix F-S.  Model Output - Simulations
                                       357
-------
Appendix F-5(a-l). Simulated Peak (five-minute) Episode for Arsenic (As) Aerosols
        Highest brief episode,  lower level




Appendix F-5(a-2).  Second-Highest 24-hour Averages for Arsenic (As) Aerosols
        2nd-highest 24-hour average
                                          359
-------
Appendix F-5(a-3).   Simulated Dry Deposition Fluxes for Arsenic (As) Aerosols, 186-day
Averages	                             	
                Dry-Deposition Rate:  Hilligrrans/hectare/day
Appendix F-5(a-4).   Simulated Wet Deposition Fluxes for Arsenic (As) Aerosols, 186-day
Averages	    	
        Average Wet-Deposition Rate:   Hilligrams/hectare/day


                                          360
-------
Appendix F-5(b-l). Simulated Peak (five-minute) Episode for Copper (Cu) Aerosols
         Highest  brief episode,  lower level


Appendix F-5(b-2).  Second Highest 24-hour Averages for Copper (Cu) Aerosols
        381 <•< 434
        224 <=< 276
        171 <1< 224
        119 
-------
Appendix  F-5(b-3).
Averages	
Simulated Dry Deposition  Fluxes  for Copper  (Cu)  Aerosols,  186-day
                                           '- - - -XXX
                                           • - - -XXXXXXXXXX
                                           yxxxxxxwxxxAxx
                                           XXXXHXXXXXXXXXX
                                           xxxxxxxxxxxxxxxxxx:
                                           XXX XXXXXXXX J& K X
                                                  xxxx
                                           xxxxxxxxxxx
                                           XXXXXXXXXXXXXXX

                                            '   x^x x
                                           XMXXXXXXXXXX
                                           XHXXXKXI-iXXKXKK
                                                                            MXX
                                                                      XMXXXXXXXXXXXXXX-•-

                                                                       x xx'XK-^XXX^X'
                                                                     XKHXKXXK'XXXXKXXXX- • -
                                                                     XKHXKXKXXMXXXKKXK

                                                                            '
                                                        XXXXXXKXXXXXXXXXXXKXXKXXXXXKXXXXXXXXXXX
                                                        XXXXXXXXXXXXXXXXXXXXXxWXXWXWXXXXXXXXXXX

                                                                                    KMX*
                                                            XXXXXXXXXXXXWXXXXXKXXKXXXHXXXXXXXXKXXXX
                                                            XXXXXXXXXXXXXHXXMXXXXXXXXXXXXXXXXMWXXXX
                                                               XXXXXXXXXXKXXXXXXXXXXXXXXXXXXXXXXX

                                                                    XXXXXXXXXXX'X'XMXXHXXXXXXX'XXX
                                                                   XXXXWXXKXXXXXXKXXXXXXXXXXXXX
                                                                         XKXXXXXXXXXXX
                                                                      xxxxxxxxxwxxxxxxxxx--••
                                                                      XXXWXKXXXWXXHXKHXXX-- - -
                                              - - - -XXXKXXXXHXXXX
          Ayerage Dry-Deposition Rate:   HilligraMS/hectare/day
Appendix F-5(b-4).
Averages	
Simulated Wet Deposition Fluxes for Copper  (Cu)  Aerosols,  186-day
          Average Net-Deposition  Rate:   nilligpans/hectare/day


                                                 362
-------
Appendix F-5(c-l.)  Simulated Peak (five-minute) Episode for Lead (Pb) Aerosols
         Highest brief episode, lower level




Appendix F-5(c-2). Second Highest 24-faour Averages for Lead (Pb) Aerosols
         2nd-highest 24-hour average
                                          363
-------
Appendix  F-5(c-3).
Averages	
Simulated Dry Deposition Fluxes  for Lead  (Pb) Aerosols,  186-day
                                                              XXXXXXXXXXXXXXX-
                                                              xxxx"x x xW x xViixx Xs-
                                                              KXXXHXXHXXXXXXX-
                                                              KKXKHXXHKKKXHXK-
                                                   XXXKXXHXXXXXXXXXXXXXXXJXXXXXXXXXXX-
                                                   XXXXXXXXXXXXHXXXXXXXXXXXXXXXXXXXX-
                                                         XXXKXXXXXMXXRXXXXXKXXXXXKXXXXXXX
                                                          (XXXXXXXMXXXXXXXXXXXXXXXXXXXXXX
         Average Dry-Deposition  Rate:   nil 1igraws/hectare/day
Appendix F-5(c-4).
Averages
Simulated Wet  Deposition Fluxes for Lead  (Pb) Aerosols,  186-day
                                          xxxxxxxx
                                 _xxxxxxxx
                              y xxx^xxx^x x'Wx xx rfxxx xW xxWW XK
                              XKXXXXXXXXXXXKXXXXXXWXXXXXXXX
         Average Wet-Deposition Rate:  Mi Migrate/hectare/day

                                             364
-------
Appendix F-S(d-l). Simulated Peak (five-minute) Episode for Zinc (Zn) Aerosols
              <6573
              <5774
              <4974
            = <4175
        Highest brief  episode* lower level
Appendix F-5(d-2).  Second Highest 24-hour Averages for Zinc (Zn) Aerosols
        2nd-highest 24-hour average
                                          365
-------
Appendix  F-5(d-3).
Averages
                 Simulated  Dry-Deposition  Fluxes for  Zinc  (Zn)  Aerosols,  186-day
300  ft<
                                 KXKXXXXXXXXXHXXXX
                                 KXX^XXXXXXXXXXXWXXXX

                                 H'XXx1*Kx xVx x xW xxHH xxxVx x
                                 KXXKXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
                                 HXXXXXXXXXXXXXXXX
                                 '.' V '.".^KX Wx'x x J&x xx^x1 Kx'Wx'x x x^xxyx' xxx^
                                 - - - -XKMXXXXKXXXXXKXXXXXXHXXXXXXXXKXXX
                                 - • - -XXXXXMXXXXXXXXXXXXXXXXXXXXXXXXXXXX:

                                     ' xx xVx x k^ x x'x^            '    '
                                     XWXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
                                  - - ..... XXXXXXXXXKXXXXXXXXXXXXXX
                                       XXXKXXXXXKKXXXXXXXXHXXHX
                                                                                   (XXXXXXXXXXXXXX

                                                                                   (xx^cxx iAcx x xS< x x
                                                                               XWXXXXXXXXXXXWXXXXXX I - - ......
                                                                            XXXXXXXXXXKXXXXXKXXXXXX
                                                                            XXXXXXXXXXXXXXXXXXXXXX
                                                                               KXXXXXXXXXXXXXXXXX
                                                                               XXXXXXKXXXXXXXXXXX
                                                                                          KWXKMXHKXXWXX-
                                                                            |priiiiXX_XXXXXXXXXXX>[XXXXXHXXXXXXXX

                                                                            xx xWxx x'xx'xi'&'xx' x^otxxx' x'x'yk' x'xMx'x x
                                                                          XXXWXXXWXXXXXXXXWXXXXHXXXXXXXXyXXX-
                                                                            XXXXWXXXXXXXXXXXXXXXXKXXXXXXXXX-

                                                                            ......  '''''^
                                                                               XXXXXXXMXXXXXXXXXXMXXXXXXXXX -
                                                                                XKXXXW
                                          ' V VJx' xHxSixxx^x X'H^XX Wx' xx
                                       ...... -XXXXXXXXXXXXXXXXX
                                       ....... XXXXXHXXXXXXXXXXX
                                                                                  XXXXXXXXXXXXXXXXXXX
                                                                                  XXXXXXXXXXXXXXXXXXX

                                                                      MX'X^X'K^
                                                                       XXXXKXXXXXXXXXlwnMXXXXXXXXXXXX
                                                                       XXXXXXXXXXXXXXXXXRKXXXKXXXXXXX

                                                               '.".".' '.v: '.".' V.'V V '.^ xitxHixxxVxxxx' x
                                                                . ' - ..... - - - -XXXXXKXXXXXKXX
                                                                         XXXXXXXXXXXXXXXXXXi
            Average Dry-Deposition Rate:
Appendix  F-5(d«4).
Averages	
                 Simulated  Wet  deposition Fluxes  for  Zinc  (Zn)  Aerosols,  186-day
           300
           106 << 300
            30 <•< 100
                        KXXX^XXXXXXXWXKKXKXJf	SXXXXXWXMXXXXXXX	1
                        XXXXXXXXXXXKXXXXXXXX^i*_*XXXXXXXXXXXXHXXX	
                        XXXXXHHXXXXXXMXXHXXX «^>i*XJiit*4^XXXXXXXXK	I
                                                              ix x1x'xx'x1xxxxxxxx'
                                  XXMXXXXXXXXXXXXXXXXXKKXXXXXHXXHXXHXXxHcxXXXXXKXXXXXK
                                  XXXXXXXXXXXmXXXXXXXXKXXXXXXXXXXXXXXXXnXXXXXXXXXXXXX
                                  	''N'''*'''"	*""
                                                              XXXMXXXKXXXXXXXXXXXXXXXXXX-•
                                                               XXXXXXMXXXXXXXXMXXXXXXMXX
                                                                    xx Hx'x x'JJx'x xs^y KX'WX'K x'
                                                                      xxxxxxxxxxxxxxxx
                                                                      xxxxxxxxxxxxxxxx
                      Wet-Deposition  Rate:   Milligraws/hectare/day


                                                      366
-------
Appendix F-S(e-l).  Simulated Peak (five-minute) Episodes for Vapor + Particulate PAH
        Highest brief episode, lower  level



Appendix F-5(e-2). Second Highest 24-hour Averages for Vapor + Particulate PAHs
        2nd-highest 24-hour average
                                         367
-------
Appendix F-5(e-3).  Simulated Dry-Deposition Fluxes for Vapor + Particulate PAH, 186-day
Average	
                                                         XXXXXXXXXXXXXXXXKXXXWXWMXXXX
                                                          X**************™****™****
        Average Dry-Deposition Rate:   nilligpans/hectare/day

Appendix F-5(e-4). Simulated Wet-Deposition Fluxes for Vapor + Particulate PAH, 186-day
Averages                 	
        Average Wet-Deposition Rate:   Hilligpans/hectare/day

                                          368
-------
Appendix F-6. Development of the Mobilization Coefficient Model	


Introduction

The following description summarizes a six-month study conducted to develop and implement a
model to provide estimates of the fractions of heavy metals and PAHs that enter Commencement
Bay in stormwater runoff following deposition  on the watershed.  These fractions, mobilization
coefficients, provided estimates of pollutant loadings from the air to the Bay via stormwater runoff
when combined with atmospheric loading values and pollutant accumulation period data.

Two groups of pollutants were investigated: heavy metals1 and polycyclic aromatic hydrocarbons
(PAHs).  Individual mobilization coefficients were to be obtained for seven metals (Pb, Cu, Zn,
As, Cr,  Ni, and Mn).  Insufficient  data were available, however, to allow the calculation of
mobilization coefficients for individual metals and PAHs.  Both metals and PAHs were assumed
to be completely associated with fine sediments, and were considered as a single sediment-bound
species,  often referred to as "the pollutant".   Average  annual  mobilization  coefficients were
computed for metals  and PAHs  for a total of  8.75 square kilometers (2,162 acres)  of the
Commencement Bay watershed.

Chemical and physical processes occur where fresh water enters saltwater that can significantly
affect the fate of waterborne contaminants.  Although consideration of these processes was beyond
the scope of this study, these processes must be considered in extrapolating from contaminant
loadings  in stormwater runoff to environmental  impacts in Commencement Bay.

Overview of the Mobilization Coefficient Model

No one model or approach was identified in the  literature search as being capable of providing the
desired mobilization coefficients for the Tacoma Tideflats study area within the  study's budgetary
and time constraints.  As a result, the following approach was developed. This model may be
described as distributed, steady state, deterministic, and empirical. The Mobilization Coefficient
Model incorporates elements of the Seattle Metro Desk-Top Model (Buffo,  1979), the Storm Water
Management Model (SWMM) (Metcalf and  Eddy, 1971), the Soil Conservation Service (SCS)
Curve Number method (SCS, 1986),  and the method of Horner et al. (1986).

From the Metro Desk-Top Model are borrowed the concepts of a "typical year", a "typical dry
(accumulation) period", and, indirectly, the pollutant washoff function from the SWMM model.
The  SCS Curve Number method is used  for  hydrology.  The techniques of superimposing a
hypothetical grid over the study area, of relating cells in this conceptual grid to cells in SMART
software  computer  spreadsheets,  and of  using the  SMART software  system  to  model
interrelationships between individual cells of the watershed grid, come from the work of Horner
et al. (1986).

Stormwater Transport Model

Unit Drainage Area Concept

The basic unit of the study area to which the Mobilization Coefficient Model is applied is the "unit
drainage area".  A unit drainage area is a  contiguous area of the watershed, lying within a cell,
which can be assumed to have uniform soil type and ground surface cover, and through which the
path of runoff can be assumed to be unidirectional. The unit drainage area is therefore the basic
watershed unit for which data must be obtained.  The next largest watershed unit in this approach
    1 The terms "heavy metal", "metal", and "toxic metal" are used interchangeably.

                                          369
-------
is the sub-basin.  A drainage sub-basin is, in turn, a subunit of a larger, natural drainage basin
having a single major outflow.   Drainage sub-basins can be either  "built", having  boundaries
determined by an engineered drainage system, or natural.

Drainage Pathway Concept

A conceptual stormwater transport model was  developed to serve as the basis of the pollutant
transport model.  A flowchart illustrating this model is given in Figure 1.  The arrows in Figure 1
correspond to what may be thought of as "unit transport pathways" (or simply,  "unit pathways"),
which describe the movement of stormwater between fundamental compartments in the model. The
same term, unit transport pathway, is used in both  the stormwater and pollutant transport models.
This use is based on an understanding that the overall pathways for stormwater and pollutants in
stormwater diverge to some extent as a percentage  of the total pollutant load is removed from the
bulk solution/suspension by a  number of processes including settling, flocculation,  filtration,
volatilization, biodegradation, hydrolysis and photolysis.

A  significant portion of the rain which falls onto pervious land  in  the Tacoma  Tideflats area
probably reaches Commencement Bay via shallow  subsurface flow.  A high  water table has been
noted in many pre-construction soil studies throughout the area, forming an effective barrier to the
downward migration of stormwater through the  soil.  Aside from ponding at the surface, the only
path of travel for stormwater is downhill towards the Bay.

Tidal effects on the groundwater elevation in the Tacoma Tideflats area can be observed at sites
several blocks  inland from  Commencement Bay and its waterways.   In the pollutant  transport
model, all metals and PAHs in stormwater  that infiltrate the soil are assumed to be bound to
sediment particles,  and are assumed to be completely removed via filtration.  Tidal effects on
groundwater are not considered in this model.

The conceptual stormwater model presented above represents an attempt to describe all of the major
routes of stormwater transport observed in the study area.  The dominant unit pathways vary from
area to area, and from cell to cell within the conceptual study area grid.  For instance, pipe flow
is more important in the developed, industrial Tideflats area north of 1-5 than it is in the semi-rural
area south of the freeway.

Surface runoff doesn't travel far in the Tacoma Tideflats area before it either enters a drainage pipe
or ditch, or infiltrates down into the soil. The flatness of this area provides little driving force for
overland flow,  thereby enhancing stormwater infiltration into the soil.

The unit drainage area concept serves to link the stormwater transport model described above to
the pollutant transport model described below. The size of unit drainage areas depends on the level
of accuracy sought.  In general, the smaller the unit drainage areas, the greater the accuracy of the
overall Mobilization Coefficient Model, up to the point at which the errors associated with other
parts of  the overall model (i.e., the SWMM washoff function, the typical year approach of the
Metro Desk Top Model,  etc.) eclipse any further increase in  accuracy achieved by a unit decrease
in the size of the unit drainage areas.
                                            370
-------
Figure 1.  Conceptual Stormwater Transport Model
                                              Rain
                                                  Impervious  P«rvlou«
1.   Rain falls directly onto the bay.
2.   Rain falls onto the land surface.
3    Runoff from an impervious surface enters a drainage pipe.
4.   Runoff from an impervious surface flows to an adjacent impervious surface.
5.   Runoff from an impervious surface enters a ditch.
6.   Runoff from an impervious surface enters a drainage pipe.
7.   Runoff from a pervious surface enters a drainage pipe.
8.   Runoff from a pervious surface flows to an adjacent impervious surface.
9.   Runoff from a pervious surface flows to an adjacent pervious surface.
10.  Runoff from a pervious surface enters a ditch.
11.  Runoff from a pervious surface enters the groundwater.
12.  Runoff enters the bay via flow over an impervious surface.
13.  Runoff enters the bay via flow over a pervious surface.
14.  Stormwater in ditch enters a drainage pipe.
15.  Stormwater in ditch enters the bay.
16.  Seepage from ditch enters the groundwater.
17.  Stormwater enters the bay via a drainage pipe.
18.  Stormwater in the pipe enters a ditch.
                                            371
-------
Pollutant Transport Model

Atmospheric contaminants are deposited onto the watershed both during the dry period preceding
the storm (dryfall) and throughout the course of the storm (wetfall). Pollutants deposited directly
onto the water surface of Commencement Bay enter the Bay without the transport losses associated
with pollutants deposited onto land  areas that are transported to the Bay  in stormwater.  All
waterways and the Puyallup River are considered part of Commencement Bay for the purposes of
this model.

During a rain storm, as a result of the kinetic energy of the falling raindrops and of the solubilities
of the pollutants present, a mixture of water and dissolved, solid, liquid and sorbed pollutants exists
upon the land surface.  If the rainfall volume exceeds  the initial abstraction, surface runoff occurs,
carrying  with it its pollutant load.  The following model  was developed to estimate the fractions
of metals and  polycyclic aromatic hydrocarbons (PAHs) in this  washed off load which reach
Commencement Bay in surface runoff.  These fractions are referred to  as pollutant delivery ratios,
or simply as delivery ratios.

The basic units of land within the study area to which pollutant delivery ratios (C,) apply are the
unit drainage areas. Cj)  denotes the composite pollutant delivery ratio for a unit drainage area.
C{p represents  the  fraction of pollutant which  is transported from the unit  drainage area to the
receiving water.  To calculate C j) for a  unit drainage area, the path of stormwater runoff from that
unit drainage area is traced to the ultimate fate of the pollutant, either in another unit drainage area
or in the Bay.  Then both the pollutant loss factor for each unit drainage area in the drainage path
and the Q for ditch flow are obtained. Cj> is the combined product of each C, for all the unit areas
in the path, including factors for ditch and pipe flow.  C, for flow in drainage pipes is assumed to
be  1.0 which means 100 percent  of the pollutants will be transferred.  No transport  losses are
assumed for bare,  impervious ditches,  corresponding again to a  C, value of  1.0.  No pollutant
transport (C, = 0) is assumed for ditches that are dry  throughout most  of the year and which have
pervious linings.  In this case, all sorbed metals and  PAHs are assumed to be trapped in the soil
matrix as stormwater in the ditch and infiltrated into the soil.  No pollutant transport  losses are
assumed for bare,  pervious ditches that contain water throughout  most of the  year,  again
corresponding to  a C, factor  of 1.0.  In this case, seepage from the ditch into the soil is assumed
to be insignificant.  No pollutant transport is assumed for  ditches with  pervious linings and which
contain substantial vegetation, corresponding to a C, factor of 0. In this case, all sorbed metals and
PAHs are  assumed to be removed by  filtration for ditches that usually contain water, and by a
combination of filtration and settling  for ditches that are usually dry.

The pollutant washoff coefficient for an entire cell,  adjusted for transport losses, is represented by
the symbol Cw*.
               * _
where:
              Cw =  area- weighted pollutant washoff coefficient for an entire cell, and
              C, =  area-weighted Q for an entire cell.


A pollutant mobilization coefficient (C^nnual) represents that fraction of pollutant (metals and
PAHs) which is washed off the land within a particular 0.25 square kilometer cell of the conceptual
grid, and which enters Commencement Bay in the runoff from a "typical storm".  (A "typical
storm" is a storm which delivers a volume of rain equal to the frequency-weighted average of the
volumes selected to  represent the four precipitation ranges for a "typical year".) In other words,
a pollutant mobilization coefficient is the average annual Cw* coefficient for a particular grid cell'
and is computed using typical year storm frequencies.


                                            372
-------
                        4
                        £  (Fi * CJ)
        (^annual  =
                        4
                        E(Fi)
where:
             CJ =     area-weighted pollutant washoff coefficient for an entire cell, adjusted for
                        transport losses, corresponding to a storm of volume selected to represent
                        the j'th precipitation range of the 4 representative precipitation volumes
                        for a "typical year".

              Fi =     typical year storm frequencies


Modeling Assumptions

As indicated above, the phase in which a given pollutant exists largely determines its environmental
fate. One of the first tasks in modeling the transport of a pollutant in stormwater is to determine
the phase or phases in which the pollutants exist under the particular environmental conditions
found in the study area.  This alone can be a major task. There are complex models to determine
the form in which even metals, which are conservative in the sense that they are not degraded by
bacteria, sunlight,  or hydrolytic reactions, and  do  not  evaporate, exist under given sets of
environmental conditions.  For nonconservative pollutants such as organics the situation is far more
complex. But this is only scratching the surface if one considers the real world situation in which
chemical equilibrium may not exist,  in which pollutants are sorbed to particles of an array of sizes
which are differentially transported in surface runoff, and in which dramatic pH changes occur from
block to block in industrial areas. Given the lack of available data for the Commencement Bay
watershed, several simplifying assumptions were made which greatly reduced the data requirements
for modeling at the expense of introducing additional uncertainties in the estimates.

The following assumptions were made to reduce the input data requirements needed to develop and
implement the Mobilization Coefficient Model in order to match available resources.

      1.  100 percent of all metals and PAHs which accumulate during a dry accumulation period
      of typical duration, are assumed to be sorbed to fine paniculate matter at the beginning of
      the next rainfall capable of producing significant washoff (volume .>_0.3 inches).

      2. A "typical" year of rainfall for the City of Tacoma, based on results from the GORAIN
      rainfall analysis program,  is assumed to represent  a typical year of precipitation for the
      Commencement Bay  watershed.  Input for the GORAIN program consisted of 20 years
      (1960-1980)  of 24-hour  rainfall data for a gauge formerly located atop the County-City
      Building  in Tacoma' s city center.

      3. Assignment of washoff function coefficients and SCS runoff curve numbers is based on
      surface cover/land use.

      4. Assumptions were made regarding the assignment of pollutant delivery  ratios to individual
      segments (unit transport pathways) of overall transport pathways through which stormwater
      (and pollutants) are transported from the "point"  of deposition on the watershed (i.e., unit
      drainage  area) to the point at which the runoff enters the Bay.
                                           373
-------
Integrated Mobilization Coefficient Model

A flow chart illustrating how the Desk Top model, the SCS—CN method for hydrology, the
SWMM pollutant washoff model and other methodologies and concepts are integrated to form the
Pollutant Mobilization model is given in Figure 2.

Both "typical year" data from the GORAIN rainfall analysis program and watershed data from both
aerial photos and site inspections comprise the input data for the SCS Curve Number hydrological
model.  Typical year data includes storm volume, frequency, and antecedent runoff condition data
for a  typical water year. The GORAIN program also provides accumulation period data needed
to convert pollutant accumulation rates, to be estimated using the WYNDvalley air quality software,
to  pollutant loading  rates  using  the  mobilization coefficients computed  by  the integrated
Mobilization Coefficient model.  Watershed  data, including land use, SCS hydrological soil group,
surface cover type, and drainage pathways  are obtained from aerial photos and site inspections.
The output of the SCS Runoff Curve Number Method are values of the stormwater runoff volume
for each cell of the conceptual grid.

The stormwater runoff volume values from  the SCS Runoff Curve Number method comprise the
input  data set for the SWMM washoff model.   The output from the washoff model are pollutant
washoff coefficient values, which represent  the fractions of particular pollutants, that are washed
off land surfaces  within particular grid cells in the study area.  Both the values from the washoff
model and area-weighted pollutant delivery ratio factors from the pollutant transport model are used
to compute values of pollutant mobilization coefficients (Cwannuals), which are the ultimate outputs
of the integrated Mobilization Coefficient Model.

Limitations

Since pollutant mobilization  coefficients have never been experimentally determined for the study
area,  there are no such values with which to compare the calculated mobilization coefficient values
from  the Mobilization Coefficient Model presented here.  Therefore,  the error associated with the
values of C^annual computed using the model cannot be precisely  determined.

A lower bound on the error associated with Genual values is provided by the standard error of
the mean for the total average area measured for each cell. This standard error was less than 3.0%
over all cells, and is insignificant compared to the following sources of error which cannot be
quantified in this study:

*•  Error associated with the "typical year"  approach to representing rainfall,

*  Error associated with the unit drainage area concept,

*  Error associated with application of the  SCS Runoff Curve Number Method for hydrology,

*•  Error associated with assuming that all metals and PAHs are bound to particles during sediment
    transport,

*  Error associated with pollutant washoff  model,

+  Error associated with the estimation of pollutant delivery ratios, and

>  Error associated with assuming that pollutant not washed off the watershed by one storm event
    is unavailable for washoff by the next storm event.

Data are not available to quantify the above errors.


                                            374
-------
Figure 2. Integrated Mobilization Coefficient Model
                 Rainfall Analysis Program
                                       Typical Year Rainfall Data
                 SCS Curve Number Method
                                       Surface Water Flow Rates
                 SWMM Washoff Model
                                       Fractional Washoff Coefficient
                 Pollutant Transport Model
                  Mobilization Coefficients
                                       375
-------
A limitation of the Mobilization Coefficient Model which deserves attention is that only the fraction
of metals and PAHs deposited onto a given cell that reaches Commencement Bay is estimated;
important natural processes occur which can affect the fate of contaminants in stormwater runoff
when this runoff is discharged to a marine environment.  Many of the parameters identified as
important in  influencing the partitioning of metals and PAHs, and the biological and photolytic
decomposition of PAHs, are different in stormwater runoff and saltwater, including sediment size
and concentration, pH, temperature, specific gravity, and depth. These factors must be taken into
account in assessing environmental and human health impacts of mass loadings of metals and PAHs
in stormwater runoff that enters Commencement Bay.


MOBILIZATION COEFFICIENT MODEL RESULTS

Mobilization  Coefficients were calculated for seven cells within the Sitcum Test Sub-basin and for
28 cells outside this area following the procedures described above.  When possible, these 35 cells
that had  Cwannual calculated through the use of the Mobilization Coefficient Model (presented in
Table F-6) were ranked in terms of  percentage  ground cover,  area use,  surface  water, soil
characteristics,  the area of the cell assessed as impervious, etc.  The other cells in the study area
had "best guess"  estimates made of Cwannual using the principles of the Mobilization Coefficient
Model (these figures are included in the Appendix).

Values of the average annual pollutant mobilization coefficients (C^nuals) for metals and PAHs
ranged from 0 to 0.1 for portions of seven cells (rlOcl2, rlOclS, rllc!2, rllclS, rllcl4, r!2c!2,
and r!2c!3)  lying within the Sitcum Test Sub-basin.  Thus, the fractions of metals and PAHs
deposited from the air onto those portions of cells lying within the Sitcum Test  sub-basin, and
which enter Commencement Bay in stormwater runoff from a "typical" storm,  are relatively small
compared to  the loadings of metals and PAHs to these areas from the air during the accumulation
period preceding the storm.

Other Areas

Results for 28 cells located outside the Sitcum Test Sub-basin are also listed in Table F-6. Values
of Cwannual  for two cells, r!2c9  and rllcll, were 0.3 and  0.2, respectively, to  one significant
figure, indicating that a significant portion of metals and PAHs, deposited  onto these ceils in the
accumulation period preceding a "typical" storm,  may be transported to Commencement Bay by
stormwater runoff.  Values of Cwannual for the remaining 26 cells indicate that the quantities of
metals and PAHs which enter the Bay in stormwater runoff from these cells following a "typical'
storm probably represent small fractions of the total masses of these pollutants deposited onto these
cells from the air.

Recommendations

Experimentally determined values of mobilization coefficients are  presently unavailable for any
pollutants within the Commencement Bay study area.  More studies are needed to obtain these
measured values of pollutant mobilization coefficients.  These measured values are needed to verify
this  study's  model and to compute  the  error  associated  with values of  pollutant  mobilization
coefficients obtained from it. Without verification and error analysis, this model can only provide
rough, semi-quantitative estimates of pollutant mobilization coefficients.
                                           376
-------
Table 1. Results of Mobilization Coefficient Model
Study Cell:
Row
8
9
9
9
9
10
10
10
11
11
11
11
11
12
12
12
12
12
12
13
13
13
14
14
14
14
14
14
14
15
15
15
15
15
15

Column
15
14
15
16
17
12
13
15
11
12
13
14
15
9
10
11
12
13
15
9
10
11
9
10
11
12
13
14
15
9
10
11
12
13
14

Cwannual
0.07
0.03
0.06
0
0
0.10
0.01
0.06
0.20
0.01
0
0
0
0.30
0.10
0.05
0.01
0.01
0.01
0.10
0.06
0.02
0.10
0.03
0.04
0
0.01
0
0
0.05
0.02
0.02
0.02
0.02
0.01

% Water
39
20
0
3
38
4
5
38
26
0
0
48
36
25
0
29
0
0
0
22
0
26
23
0
10
20
0
0
0
39
0
0
14
14
0

Cell Loading Factor %
40
20
6
3
40
10
6
40
40
1
0
50
40
50
10
30
1
0
1
30
6
30
30
3
10
20
1
0
0
40
2
2
20
20
1
                                          377
-------
Further Applications

The amount of pollutants washed off the land  into the bay is related not only to the percent
mobilized (mobilization coefficient) but also to the percent of the area or cell under consideration
that contains open water (direct access to the bay).  The cell loading factors presented in Table
L2 are a combination of the Genual and the percent of the cell that is open water.

Results  from the Mobilization Coefficient Model indicate that, overall, only small fractions of the
metals and PAHs which are deposited onto the Tacoma Tideflats area of the Commencement Bay
watershed during the accumulation period preceding a  "typical" storm event,  reach the  Bay in
stormwater runoff.  Factors which contribute to the relatively low C^^nnual values for metals and
PAHs in the Tacoma Tideflats area include the existence of significant areas of vegetated open
space, unlined, vegetated drainage ditches, and the flatness of the land.  Significant fractions of
metals and PAHs of atmospheric origin may be transported to receiving waters from sub-basins of
urban watersheds having, separated sewer  systems, no vegetated open spaces,  and steep  slopes.
In such watersheds, there is little filtration capacity to remove sorbed contaminants from stormwater
and more erosive energy associated with the stormwater resulting from higher flow velocities.  In
the Puget Sound area, the city centers of Seattle, Tacoma, and  Everett are examples of areas where
substantial fractions of  metals  and PAHs of atmospheric  origin may enter Puget  Sound  in
stormwater runoff.

Another factor which contributed to the low predicted values of Genual for metals and PAHs is
the annual rainfall pattern associated with  the Pacific Northwest.  The Mobilization Coefficient
Model predicts little contaminant washoff by the small storms which dominate the annual rainfall
pattern  here.   Greater values of Genual would be predicted  for areas having more  storms  of
larger volume, even if the average total annual  rainfall is less  than  it  is here (34-35 inches per
year).  Based on this  consideration, larger values of Cwannual for metals and PAHs  would,  in
general, be expected for urban areas of cities in  the Southeastern United States.
                                            378
-------
Appendix G.  Comparison of Results
     G-l.  Plots of Metal Particulate Concentrations, Metal Deposition Rate,
          PAH Particulate Concentrations, and PAH Deposition Rate
          for Sea-Land, Riverside, and Tyee Marina	381
     G-2.  One-Dimensional "Contour" Plots of Measured TSP and
          Simulated PM10	389
     G-3.  Contractor Reports and Publications Assessing Performance
          of WV3 Model	401
     G-4.  Covariance Analysis	403
     G-5.  Tracer-Rose	409
                                      379
-------
Appendix G-l.  Plots of Metal Particulate Concentration, Metal Deposition Rate, PAH
Particulate Concentrations, and PAH Deposition Rate for Sea-Land, Riverside, and Tyee
Marina.
                                       381
-------
Appendix G-l(a).  Metal Particulate Concentration (ng/m3) at the Sea-Land Site.
200
150
100
50
12/11/89
*
7
8/14/89 /
*> 1 1/16/89 /
"-" \ .-"•
	 i 	 v1
\ / /
i • •
A " " ^" ^
Arsenic
Chromium
Manganese
Nickel
Lead
Zinc
A

Dates
Appendix G-l(b). Metal Deposition Rate Oig/mVday) at the Sea-Land Site.
3,500
3.000
2,500
2,000
1,500
1,000
500
n

	 9/7/89 	
r
T/OT/QQ 1
A. /
• \
7 \ /
' 	 7 	 \ 	 / 	
1 \ !/
^ ,-••!

Arsenic
Chromium
Manganese
Nickel
Lead
Zinc
A
                                  Dates
                                       383
-------
Appendix G-l(c).  Metal Particulate Concentration (ng/m3) at the Riverside Site.
200
150  -
100  -
                                   Dates
Appendix G-l(d).  Metal Deposition Rate (/tg/mVday) at the Riverside Site.
 80
 60
 40
 20
               7/27/89
                               9/07/89
              .


                                                             A.    A
                                                       ™.../^S  ,....:..
      I	I
                 r i  y-r
                                    Dates
                                                                             Arsenic
                                                                               Q	

                                                                           Chromium
                                                                           _ — Q— _

                                                                           Manganese
                                                                           ... A ...

                                                                             Nickel
                                                                              Lead


                                                                              Zinc
                                                                             Arsenic
                                                                                Q

                                                                            Chromium
                                                                            — — D- —

                                                                            Manganese
                                                                            . . . A . . .

                                                                              Nickel
                                                                              Lead

                                                                              Zinc
                                        384
-------
Appendix G-l(e). Metal Particulate Concentration (ng/m3) at the Tyee Marina Site.
300
250
200
150
100
 50
                                                                12/11/89
                              9/1VS9
 Arsenic
    o

Chromium
                                                                         Manganese
  Lead


  Zinc
                                  Dates
Appendix G-l(i). Metal Deposition Rate Qtg/mVday) at the Tyee Marina Site.
150  -
100  -
 50  -

7/27/89
" n : :::::::
/ \
. \ 11/30/89
A.... A -a.
, ~^^ ^r^
Arsenic
Chromium
_ — D— _
Manganese
Nickel
Lead
Zinc
A


                                   Dates
                                       385
-------
Appendix G-l(g).  PAH Participate Concentration (ng/m3) at the Riverside Site.
25
20
15
10
                                                         12/11/89
  i
 fr:
 If
it
                                                   •V
                                                   6? I
                  Naphthalene
                   ^^^•^^^M^^^^

                 Phenanthrene
                   	D- -

                 Fluoranthene
                   . . . A . . .

                    Pyrene


                   Chrysene
                                Dates
Appendix G-l(h). PAH Deposition Rate (ng/mVday) at the Riverside Site.
q nnn

o enn
£,3UU
9 nnn
i *^nn
i nnn
*^nn
0


	 12/14/89
8/24/89 •
	 	 A, 	 /
/ \ /
•' A'.. / •'
_ 	 / 	 (f.:.:,.-A 	 '$. !/
M* • JP KB^^H ^ ^_ • ^f
i i fc~l JT~ r £^rt^t^I_^_i.. i i i i i i i T i i i i

Naphthalene
Phenanthrene
Fluoranthene
Pyrene
Chrysene



                                 Dates
                                       386
-------
Appendix G-l(i).  PAH Participate Concentration (ng/m3) at the Tyee Marina Site.

80
60
 40
 20
                                                             12/11/89
                                                             /   !
                                                            I	j.
                                        //    !
                                                        •
                                                      Naphthalene
                                                          Q

                                                      Phenanthrene
                                                      Fluoranthene

                                                        Pyrene

                                                       Chrysene
                                 Dates
Appendix G-1Q').  PAH Deposition Rate (ng/m2/day) at the Tyee Marina Site.
10,000
 8,000
 6,000
 4,000
 2,000
                                                            12/11/89
                                                       /r*-.  ./
                       8/24/89

       I	I
          i

fetfcg'Jrfa^t	f-r-*
                                                     Naphthalene
                                                          Q

                                                     Phenanthrene
                                                     Fluoranthene

                                                        Pyrene

                                                       Chrysene
                                  Dates
                                       387
-------
Appendix G-l(k).  PAH Particulate Concentration (ng/m3) at the Sea-Land Site.
25
20
15
10
                                                            12/11/89
                                                11
                                               I/

                                              it

                                             it

                                            V
                                            Si   i  -
                                                               Naphthalene
                                                                   Q

                                                               Phenanthrene
                                                                _ _o	

                                                               Fluoranthene
                                                                ... A ...

                                                                 Pyrene


                                                                Chrysene
                                 Dates



Appendix 6-1(1). PAH Deposition Rate (ng/mVday) at the Sea-Land Site.

8,000
6,000
4,000
2,000
                                                              12/14/89

                                                                    I
                              9/07/89
                                                          I
7/13/89

	\	
                             /'
                            //'
              -       J3- -
              ,V7  ,   L
                            .   i  i   i  i   i  4  i
                                                               Naphthalene
                                                                   Q -

                                                              Phenanthrene
Fluoranthene
 ... .A ...

  Pyrene



 Chrysene
                                  Dates
                                         388
-------
Appendix G-2. One-Dimensional "Contour" Plots of Measured TSP and Simulated PM1(I.


Solid lines connect the observations.  The points with the larger circles are simulations by
WV3.
                                        389
-------
  188
    B
  188
                                                                     6-29
    B
  188
                                                                     7-B3
                                                                     7-86
  Brown      Tyee    Horse
                      FSI12
                       SeaLn
                                         Alex
  River
188
  B
188
                                                                    7-18
                                                                    7-13
188
  8 E
                                                                    7-17
Brown      Tyee    Horse
                    FSI12
                     SeaLn
                                       Alex
River
                                       391
-------
  188


ug/BA3
    8
  188
ug/BA3
                             7-28
    8
  188
                           o   O
                                                                      7-24
                                                                      7-27
Broun      Tyee
                         Horse
                          FSI12
                           SeaLn
Alex
River
   188
     8
   188
                                                                       7-31
     8
   188
                                                                       8-83
                                                                       8-87
 Broun      lyee
                          Norse
                           FSI12
                            SeaLn
 Alex
 River
                                          392
-------
  188
    8
  188
                                                                     8-18
ug/n*3
    e
  188
                                                                     8-M
      Broun
                                                                     8-17
        Norse
         FSI12
          SeaLn
                                        Alex
                                            River
  188
    8
  188
                                                                     8-21
    8
  188
                                                                     8-24
      Brown
                                                                     8-28
Tyee
Horse
 FSS12
  SeaLn
Alex
River
                                    393
-------
  188
    B
  188
ug/nA3
    6
  188
                                                                      9-81
                                                                      9-85
                                                                      9-87
      Broun
Tyee
                   Norse
                    FSI12
                     SeaLn
Alex
River
  188
   8
  188
                                                                     9-11
    8
  188
                                                                     9-14
                                                                     9-18
Broun      Tyee    Horse
                    FSI12
                     SeaLn
                                        Alex
                                                    Riwer
                                    394
-------
  180


ug/*A3
    B
  188
    B
  188


ug/n*3


    6
                                                  9-21
                                                                      9-25
                                                  9-28
Brown      Tyee    Horse
                    FSI12
                     SeaLn
                                         Alex
                                                  River
    188
                                                                        18-82
      B
    188
                      o
                                                                        18 Bu
     168
         Brown
Tyee    Norse
         FSS12
          SeaLn
                                            Alex
                                                                         18-89
                                        395
-------
  188
    8
  188
                                                                      18-12
ug/«A3
    8
  188
                                                                      18-16
                                                                      18-19
Brown      Tyee    Norse
                    FS112
                     SeaLn
                                         Alex
River
   188
     8
   188
                                                                       18-23
     8
   188
                                                                       18-26
                                                                       18-38
 Brown      Tyee
                           FS112
                            SeaLn
                                          Alex
 River
                                       396
-------
 188
                                                                     11-82
 188
   8
 188
                                                                     11-86
    Brant
        Horse
         FS112
          SeaLn
                                                                     11-89
                                        Alex
                                             River
188
  8
188
                                                                    11-13
  8
188
                                                                    11-16
                                                                    11-28
    Broun
lyee
Horse
 FSI12
  SeaLn
Alex
River
                                      397
-------
  188


ug
-------
  188
  188


119/11*3


    8
  188


119/11*3


    8
                                                                  12-13
                                                                 12-14
      Brown       Tyee    Norse
                           FSI12
                            SeaLn
                                    Alex
                                              River
  188


ug/n*3


    8
  188


ug/n*3
                                                                  12-15
    8
  188
                                                                  12-16
119/11*3
                                                                        12-18
                                                                           o
Brown
                  lyec
Norse
 FSI12
  SeaLn
                                    Alex
River
                                       399
-------
188
                                                                    12-21
  8
188
  e
188
                                                                    12-23
                                                                   12-25
    Brown      Tyee    Horse           Alex                         River
                        FSI12
                         SeaLn
                                   400
-------
Appendix G-3.  Contractor Reports and Publications Assessing Performance of the WV3
Model.
Harrison, H.  1990. On the sensitivity of an air-quality dispersion model to the quality of wind
and source data.  Presented at the Pacific Northwest International Section of the Air and Waste
Management Association meeting, Portland, Oregon, November 1990.

Harrison, H.   1990.  Modeling wet and dry depositions of toxic tracers into the watershed of
Commencement Bay.  Presented at the Pacific Northwest International Section of the Air and
Waste Management Association meeting, Portland, Oregon, November  1990.

Harrison,  H.  (in press).  Where does it come from?  Polar "fluxgrams" for air-quality
management.  Journal of the Air  and Waste Management Association.

Harrison, H.  1991. Further studies of aerosol observations and simulations at Commencement
Bay: July 1983-Jan 1990.  Report to the Puget Sound Water Quality Authority.  May 26, 1991.

Harrison, H.   1991. letter report to the Puget Sound Water Quality Authority. June 9, 1991.
                                         401
-------
Appendix G-4.  Covariance Analysis
Concentrations of a suite  of metals, anions, and  PAH compounds  at  six sites  have been
measured during half-weekly intervals in the summer, fall, and winter of 1989.  These data
have  been analyzed for their  spatial and temporal patterns  and compared with computer
simulations that attempt to estimate similar spatial and temporal patterns from assumptions about
the sources, dispersion, and deposition.

Another  way of  looking  at the same data  is to  analyze  the covariances between the
measurements.  That  is,  one may "factor"  correlations among the  observables into linear
combinations that behave similarly in time or space.  Often, examination of these factors reveals
sensible patterns that relate to the physics  of the emissions and transport.

Covariance analyses may be attempted in several ways. In the present case we might consider
hunting for spatial patterns by averaging the observations over time, or for temporal patterns
by averaging over space. This latter choice, however, is discouraged in the present case owing
to the requirement that spatial correlations among samples collected at the same times would
have to be averaged over six or fewer  sites. Because sampling errors in correlation coefficients
vary  approximately as l/sqr(N-4), where N  is the number  of independent  observations,
uncertainties in temporal correlations  from averaging over the six sites must equal or exceed
l/sqr[6-4] =71 percent. For this reason, we have instead examined the data to seek co-varying
linear combinations of the tracers, averaged over time at all sites.

In the first section below we describe  this process for metals and certain anions. The next we
discuss correlations and factors for the PAH compounds.  The third  section describes factor
analyses of both tracer types simultaneously, and the fourth describes some attempts to extract
temporal and spatial information for the factors.  We conclude with some general remarks.

Metals and Anions

In Table G-4(a) and the similar tables that follow, the analysands (S, Cl, ...) were normalized
to relative fractions of unity before the correlations.  The rows in Table G-4(a) are labeled in
the same sequence as  the columns; thus the  correlation between S  and  itself is unity (in the
upper left corner of the table entries), that of S with Ca is -0.6 (row 1, col 4), that of Cl with
K is -0.4 (row 2,  col  3), and so on.  Sampling errors for the correlations were ±.0.14.  To
present this table  on one page,  only one digit is  shown for each entry;  three digits were
retained, however,  for the calculations that follow.

Various numerical techniques may be  used to  "diagonalize" correlation matrices, such as Table
G-4(a).  A complete eigenvalue/eigenvector "rotation" seeks in turn those linear combinations
of the observable tracers (S, Cl, ...)  that are mutually orthogonal and minimize the residual
variance, vector by vector.  Owing to the large internal errors for each  coefficient, however,
we have chosen instead an iterative Jacobi rotation and to truncate the diagpnalization process
when the largest off-diagonal term was less than 0.24, twice the mean sampling errors of single
coefficients in Table G-4(a). The result of this exercise is Table G-4(a).
                                          403
-------
Table G-4(a).  Correlation Matrix for 15 Tracers Averaged Over All Sites and Times
S Cl K
1.0 0.0 -0.1
0.0 1.0 -0.4
-0.1 -0.4 1.0
-0.6 -0.5 -0.1
-0.5 -0.5 0.6
0.2 -0.0 0.2
-0.3 -0.1 0.5
0.0 -0.4 0.7
-0.6 -0.6 0.3
0.2 -0.1 0.3
0.3 -0.1 0.1
0.0 -0.0 0.1
0.4 -0.2 0.3
0.1 -0.2 0.1
0.4 0.2 0.3
Ca
-0.6
-0.5
-0.1
1.0
0.4
-0.2
0.0
-0.3
0.3
-0.3
-0.5
-0.1
-0.5
0.0
-0.6
Ti
-0.5
-0.5
0.6
0.4
1.0
-0.2
0.4
0.4
0.6
-0.0
0.0
0.0
-0.1
0.0
-0.3
V
0.2
-0.0
0.2
-0.2
-0.2
1.0
0.0
0.1
-0.1
0.5
0.1
0.0
0.3
0.1
0.5
Cr
-0.3
-0.1
0.5
0.0
0.4
0.0
1.0
0.5
0.3
0.4
0.2
0.1
0.2
0.2
0.0
Table G-4(b). Eigenvalues, Fractional
Sites and Times
Eigenvalues


Fractional Variances
Eigenvectors






























4
0
0
0
0
-0
-0
0
0
0
-0
0
0
0
0
0
0

.079
.272
.267
.017
.093
.338
.133
.231
.128
.374
.018
.332
.411
.000
.411
.168
.319


















Mn
0.0
-0.4
0.7
-0.3
0.4
0.1
0.5
1.0
0.4
0.5
0.6
0.1
0.7
0.3
0.4
Fe
-0.6
-0.6
0.3
0.3
0.6
-0.1
0.3
0.4
1.0
0.0
0.1
0.1
0.1
0.1
-0.2
Ni Zn
0.2 0.3
-0.1 -0.1
0.3 0.1
-0.3 -0.5
-0.0 0.0
0.5 0.1
0.4 0.2
0.5 0.6
0.0 0.1
1.0 0.4
0.4 1.0
-0.0 0.0
0.5 0.7
0.2 0.4
0.4 0.3
Se
0.0
-0.0
0.1
-0.1
0.0
0.0
0.1
0.1
0.1
-0.0
0.0
1.0
0.0
-0.2
0.2
Pb
0.4
-0.2
0.3
-0.5
-0.1
0.3
0.2
0.7
0.1
0.5
0.7
0.0
1.0
0.4
0.6
Variances, and Eigenvectors, for 15

3.539
0.236
-0.263
-0.372
0.427
0.231
0.427
0.000
0.311
0.319
0.389
0.101
0.027
0.000
0.027
0.000
-0.113



















1.077
0.072
-0.053
0.000
0.000
0.068
0.000
0.786
0.000
-0.222
0.000
0.460
-0.235
0.000
-0.235
0.000
-0.067



S
Cl
K
Ca
Ti
V
Cr










As
0.1
-0.2
0.1
0.0
0.0
0.1
0.2
0.3
0.1
0.2
0.4
-0.2
0.4
1.0
0.1
Tracers










Br
0.4
0.2
0.3
-0.6
-0.3
0.5
0.0
0.4
-0.2
0.4
0.3
0.2
0.6
0.1
1.0
, All










Mn
Fe
Ni
Zn
Se
Pb
As
Br





















Only the first three columns (of 15) have been retained in Table G-4(b), for those columns with
eigenvalues exceeding unity. The other columns are no more significant that would be expected
by chance from an assembly of random numbers.  Table G-4(b) suggests that for the principal
eigenvector (the left column) positive analysands with  "loadings"  greater than 0.28 (twice the
sampling error)  vary  coherently with one another, and anti-coherently with analysands that
display loadings less than 0.28. Thus, approximately in decreasing order of loading:
       Vector 1
       Vector 2
       Vector 3
Pb + Zn  + Mn +  Ni + Br + [S] - Ca
Ti + Fe  + Mn +  Cr + K -  Cl  - [S]
V + Ni
                                         404
-------
Note that the bracketed entries for [S], above, are included as interesting, but marginally below
the selection  threshold.

The first vector contains lead, zinc,  manganese, and bromine,  tracers that are strongly (but not
uniquely) identified with automotive sources.  Approximately 27 percent of the total variance
is associated  with this vector.

The  second   contains  titanium,  iron,   and  manganese,  tracers  associated  with  soils.
Approximately 24 percent of the total variance is associated with this second vector.

The third contains vanadium, a tracer associated with petroleum combustion.  Approximately
7 percent of  the total variance is associated with this vector.  This fraction is only  marginally
greater than would be anticipated from a vector of random numbers.

The grouping of metal and  anion tracers  revealed  by this  analysis is sustained  (within
uncertainties  set by relatively larger sampling errors) by similar analysis at the  Alexander
Avenue site,  only:

In which:
       vector 1  :      Mn + Ni  + Pb  +  Zn + Br - Ca  - [S]
       vector 2  :      Fe  + K   + Ti  - Cl

This agreement is not surprising, however, as the data at Alexander Avenue comprise much of
the same data subsumed into the correlations at all sites.   Strictly speaking, the loadings for
none  of the  vectors at Alexander  Avenue  exceed the two-sigma criterion imposed  for the
decomposition of all the data together.  Sampling errors among the correlations at Riverside,
Tyee, and Morris Industrial exceed  0.7, and equal unity at Browns  Point and Sea-Land. Thus
it is not possible from these data to use time-averaging factor analyses of the metal and anion
measurements to distinguish differing types of emissions at the individual sites of our study.

Table G-4(c).   Eigenvalues, Fractional Variances,  and  Eigenvectors for 15 Tracers,
Alexander Avenue Site Only

               Eigenvalues
               5.335         3.304

               Fractional Variances
               0.356         0.220

               Eigenvectors
               0.317        -0.172      S
               0.000        -0.405       Cl
               0.083         0.453       K
              -0.325         0.181       Ca
              -0.193         0.388       Ti
               0.241         0.201       V
               0.000         0.249       Cr
               0.380         0.177       Mn
              -0.083         0.453       Fe
               0.380         0.177       Ni
               0.345        -0.031       Zn
               0.161         0.000      Se
               0.366         0.170      Pb
               0.000         0.000      As
               0.342        -0.134      Br

                                           405
-------
Correlations and Co-factors for PAH Compounds

Table G-4(d) presents the crossed-correlation matrix, averaged over all sites and times, for 17
PAH compounds, with vapor and aerosol measurements combined at each site.  As with Table
G-4(a) only one  significant digit is shown here,  but  three  digits were preserved for the
eigenvector analysis that follows.


Table G-4(d).  Correlation Matrix for PAH Compounds (Vapor + Aerosols) at All Sites

Minimum standard error =  .144
1.0 0.9
0.9 1.0
0.4 0.6
0.7 0.9
0.7 0.8
0.6 0.7
0.7 0.8
0.5 0.6
0.5 0.6
0.6 0.8
0.5 0.7
0.3 0.6
0.7 0.8
0.8 0.8
0.8 0.9
0.3 0.6
0.8 0.9
0.4
0.6
1.0
0.5
0.8
0.8
0.8
0.8
0.8
0.7
0.8
0.7
0.6
0.6
0.6
0.6
0.6
0.7
0.9
0.5
1.0
0.6
0.6
0.6
0.5
0.6
0.7
0.6
0.6
0.7
0.7
0.7
0.6
0.7
0.7
0.8
0.8
0.6
1.0
1.0
0.9
0.9
0.9
0.9
0.9
0.7
0.8
0.8
0.8
0.6
0.8
0.6
0.7
0.8
0.6
1.0
1.0
1.0
1.0
1.0
0.9
0.9
0.7
0.8
0.8
0.8
0.7
0.8
0.7
0.8
0.8
0.6
0.9
1.0
1.0
0.9
0.9
0.9
0.9
0.7
0.8
0.8
0.8
0.6
0.8
0.5
0.6
0.8
0.5
0.9
1.0
0.9
1.0
1.0
0.9
0.9
0.8
0.7
0.7
0.7
0.7
0.7
0.5
0.6
0.8
0.6
0.9
1.0
0.9
1.0
1.0
0.9
0.9
0.8
0.8
0.7
0.7
0.7
0.7
0.6
0.8
0.7
0.7
0.9
0.9
0.9
0.9
0.9
1.0
1.0
0.9
1.0
0.9
0.9
0.8
0.9
0.5
0.7
0.8
0.6
0.9
0.9
0.9
0.9
0.9
1.0
1.0
0.9
0.9
0.8
0.8
0.9
0.8
0.3
0.6
0.7
0.6
0.7
0.7
0.7
0.8
0.8
0.9
0.9
1.0
0.8
0.7
0.7
1.0
0.7
0.7
0.8
0.6
0.7
0.8
0.8
0.8
0.7
0.8
1.0
0.9
0.8
1.0
1.0
1.0
0.8
1.0
0.8
0.8
0.6
0.7
0.8
0.8
0.8
0.7
0.7
0.9
0.8
0.7
1.0
1.0
1.0
0.7
1.0
0.8
0.9
0.6
0.7
0.8
0.8
0.8
0.7
0.7
0.9
0.8
0.7
1.0
1.0
1.0
0.7
1.0
0.3
0.6
0.6
0.6
0.6
0.7
0.6
0.7
0.7
0.8
0.9
1.0
0.8
0.7
0.7
1.0
0.7
0.8
0.9
0.6
0.7
0.8
0.8
0.8
0.7
0.7
0.9
0.8
0.7
1.0
1.0
1.0
0.7
1.0
naph
acny
acne
flor
phen
anth
fluo
pyre
baa
chry
bbf
bkf
bap
indp
dba
bzpe
bep
Note  that all the correlations are positive and that  most of them exceed 0.5.  This is not
surprising, because most of the PAH compounds are  emitted nearly synchronously by a single
source.   The effect of this in factor analyses is that all the 17 PAH compounds collectively
behave as if they were a single, generic PAH tracer.
                                         406
-------
Table G-4(e).  Eigenvector Decomposition of Table G-4(d)
              Eigenvalues
              13.188       1.210

              Fractional Variances
              0.766        0.070

              Eigenvectors
              0.191        0.674       naph
              0.232        0.034       acny
              0.217       -0.029       acen
              0.203       -0.027       flor
              0.253        0.038       phen
              0.260        0.039       anth
              0.258        0.039       fluo
              0.262        0.039       pyre
              0.262        0.039       baa
              0.274        0.037       chry
              0.251        0.037       bbf
              0.230       -0.419       bkf
              0.265        0.035       bap
              0.241        0.035       indp
              0.236        0.034       dba
              0.225       -0.593       bzp
              0.245        0.036       bep


Note that the first vector, which accounts for 77 percent of the variance, contains nearly equal
loading coefficients for each of the 17 PAH tracers.  This vector represents the bland average
of all these tracers, the generic PAH factor.

The second  vector, which is only marginally more  significant than would be expected from
arrays of random  numbers (if even that) accounts for 7 percent of the variance, with high
loading factors for

        vector 4    :       all the PAH  compounds
        vector "X"  :       naphthalene  - benzo(k) fluoranthene
                                       - benzo(g,h,i) perylene

The first of the tracers in the "X" vector, naphthalene, is poorly measured by our analytical
technique: it is likely that the inclusion of this tracer in vector "X" results from measurement
variance rather than from real physics in the emission and transport.

The possibility remains open,  however, that benzo(k) fluoranthene and benzo(g,h,i) perylene
may behave sufficiently differently from the generic PAH to permit their use as a discriminator
of different sources, as for example between the Kaiser plume and woodstove or hogged fuel
emissions.

Co-factor Analyses  of All the Tracers

The grand correlation matrix for the 15 metals and anions plus the 17 PAH compounds results
in a bulky 32 x 32 table that is substantially block-diagonal, with relatively little mixing between
the metal/anion and PAH components.  Factor decomposition of this correlation matrix reveals


                                          407
-------
the same tracer groupings as those displayed when each block is factored independently, with
the exception that second PAH vector now mixes with selenium.

       eigenvalue          =  1.618
       fractional variance = 0.050
       vector:"X"  0.51  * selenium
                 + 0.58  * naphthalene
                  - 0.46  * benzo(k) fluoranthene
                  - 0.43  * benzo(e)  pyrene

Again, this vector is only  marginally significant: ensembles of random numbers could be
expected to generate equal or higher fractional variances with odds near 1:3.

Spatial and Temporal Patterns

While constraints of signal-to-noise with the present data require that the primary factorization
must be made by averaging  over all  sites  and all  times, the factors  so determined may
nevertheless still be  evaluated at each site and each time.  The inherent noise remains, but
simple spatial and temporal  patterns may perhaps still be discerned.

In the present case, however, supportable conclusions from this exercise are fairly limited:

a.  The relative contributions of vector [1], associated with automotive transport,  is higher at
Browns's Point and Riverside, the most northerly and most southerly of the sites, and lower at
Morse Supply and at Alexander Avenue.

b.   Conversely, the relative contributions of vector  [2],  associated with soil minerals,  was
lowest at Brown's Point and Riverside, and highest at Morse and Alexander.

c.  The relative contributions of both  marginal vectors [3] and  "X" were  highest at Brown's
Point. The former was lowest at Morse, the latter at Alexander.

With these tentative observations and the discussion  that follows, it should be noted that the
absolute vectors are linear combinations of measured concentrations, with each tracer weighted
inversely by the standard deviation of the measurements for that tracer, determined over all the
samples  and all the sites.  The relative vectors, however,  are normalized to unit sums. Thus
if, for example, the absolute vector for the soils component [2] at Brown's Point decreases with
greater distance from the Tideflats, the relative vector for cars [1] increases as a consequence
of its definition.

The behavior of vector  "X", however, is a little more interesting and seems to indicate that (if
real) it is NOT a tracer of the industrial core.

Not very convincing temporal patterns could be discerned among the vectors at the several sites,
with the tentative exception that relatively LOW values of the "X" vector (in comparison to the
generic PAH) were present at Riverside during the severe  stagnation episode of December 11,
and relatively high values at Brown's Point for a sample ending  on September 11 that included
several days of light and meandering westerly winds.  It is of possible interest that September
10th marked the rather abrupt transition between westerly summer winds and the southerly fall
and winter Winds that characterized the second half of our sampling  period (see Figure 9-5??).
The low value for "X"  at Riverside during a stagnation event argues that this vector is not a
tracer of woodstove combustion.
                                          408
-------
Appendix G-5.  Tracer-Rose
A novel hybrid source-receptor model is described, and used to explore the sensitivities of WV3
to the meteorology and to the source distributions.  The new model may be generally useful.

TRACER-ROSE

Source models start with stacks and winds and follow the puffs in time and space.  Receptor
models compare "fingerprints" to match suspected sources. As with source models, the present
hybrid starts with wind Velocities and  directions; as with receptor models, it optimizes a mix
of upwind sources that best reproduce measured tracer concentrations.  The output is a "tracer-
rose": a polar plot with amplitudes proportional t the velocity corrected sensitivities of the local
tracer measurements to wind directions.  Instead of "fingerprints" it "finger points".

Specifically, the new model (tracer-rose) searches for a minimum of the function:

       V = <{[Yobs(i) - Ymod(i)]/[Yobs(i) + Ymod(i)]}2>                           [1]

                        4- [a Bias term, discussed below]

In equation [1], i indexes daily measurements, the < brackets > denote averages over i, Yobs(i)
are observations of tracer concentrations at receptor sites, and

       Ymod(i) = < W(i j) . D(i,j). A(k,j)  >                                        [2]

In equation  [2], the  denote averages over j, the hourly measurements of the wind
directions and velocities.  The W(i,j) term corrects for effects of wind velocities, the D(i,j) term
accounts for a daily  cycle of ventilations and  diffusivities,  and the A(k,j) term contains the
azimuthal pattern.  Equation [2] is not arbitrary, but results as a special case of a two-box
Eulerian-grid dispersion model, in a steady state, in which the horizontal and vertical diffusivity
coefficients  are proportional to the  wind  velocities and box dimensions.

For wind-velocity correction, tracer-rose assumes:

       W(i,j) = l/(U(i,j) + Co)                                                      [3]

where the U(j) are measured hourly wind velocities, and Co is a "meander velocity" to be
determined through the regression.

For the daily  modulation, tracer-rose assumes:

       D(i,j) = 1 + CLCos(theta) + C2«Sin(theta)                                    [4]

In equation [4], theta = (j/24.360) degrees, and Cl and C2 are two more variables for the
regression.   The D(i,j)  account both  for  variations in the daily emission patterns and for
variations in the vertical diffusivities.  A similar term appears in WV3, as P(0).

Various ways have been explored to parameterize the azimuthal term A(k,j).  It seems intuitive
that expansion in sines and cosines would be appropriate.  Tracer-rose started this way and may
return to it, but some aliasing difficulties that result when the expansion is  truncated at low
order (as it may be) and ambiguities in assigning uncertainties to the resulting patterns have led
instead to:
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                A(kj)  =  C3  + C(3+k) . F (ij,k)                                    [5]

where             C3  =  a constant isotropic component;

                  C(4)  =  a component when the winds are northerly,  [k=l];

               C(3+k)  =  are components when the winds are from other sectors, respectively
                           displaced from north in a clockwise (compass) convention, usually
                           with 16 bins for the full 360 compass degrees;

and            F(i,j,k)  =  1   if the wind direction, Dir(iJ), is in the k-th azimuthal sector;

and            F(i,j,k)  =  0   if not.

Three added options complete a specification of Ymod(i): weights,  bias, and shuffle.

Weights

The hourly averages  of j in equation [2] may  be uniformly weighted,  so  that the resulting
azimuthal pattern will reflect those tracer fluxes actually measured  at the receptor, that result
from the real distribution of the wind directions.  Let me call this choice the "natural weights".
These are appropriate when you wish to identify those upwind sources that actually contributed
most of the tracer perceived at the receptor.

Alternatively, the  weights may be renormalized to simulate the distribution of fluxes through
the receptor that would have been perceived if the  winds were equally probable in each sector.
Let me call this choice "isotropic weights."   These are  appropriate  when you wish to map all
the surrounding sources, scaled to  their intensities but  roughly independent  of any particular
sample of the wind-direction distribution.

Bias

Regressions  extract information from measurements  (in this case  from winds and tracer
concentrations)  and attribute information  to derived  coefficients  (in  this case  C's).   For
regressions to make physical sense, you must have more information on the input side than you
attribute at the output.  In the present case, for example, 73 daily concentration measurements
at Fire Station No. 12 in the fall and winter of 1985 display a  serial correlation lag of 3.4 days.
The total input "degrees of freedom" (think of this as "information content", or the number of
truly independent  measurements) are therefore approximately:

       df(input)  = 73/3.4 = 23.5                                                   [6a]

If one wishes to extract a meander velocity (Co), two daily modulation coefficients (Cl and C2)
(spectator coefficients),  and sixteen coefficients to describe  the  angular pattern of A(k,j) in
sectors of 22.5 degrees, then one must expend 20 degrees of freedom and have left only:

       df(net)    = 23.5 - 20 = 3.5                                                  [7a]

But it is not enough in any regression simply to find a set of output coefficients. One must also
estimate their precisions. To do this we need at least one additional degree of freedom for each
derived coefficient. But the cruel accounting of equation [7] shows that we are bankrupt. What
to do?  Obviously, either increase or reduce expenditures.

For the first choice, we can do the accounting again with 1986 data, for which we have 355
nondefault days that display a serial correlation  lag of 2.1 days, for which

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       df(input)  = 355/2.1 =  169                                                 [6b]

With 20 coefficients, each with 20 more standard errors,

       df(net)    = 169 - 2(20) = 129                                              [7b]

Alternatively, if we must,  we can spend less.  If we restrict ourselves  to eight azimuthal
coefficients, plus the four spectators, then with the data from the fall of 1985,

       df(net)    = 73/3.5  - 2(8 + 4)  = -0.5                                       [7c]

Actually,  the accounting is  a little bit worse than we have made it out to be, because the
distribution of wind directions may undersample some of the azimuthal bins.  So we are still
in trouble. What to do now?

One approach is to reduce our angular resolution still further say to four bins, or we can
use the following alternative:

Equation  [1] lists a "bias"  term  The idea here is to put the derived  azimuthal coefficients
through a smoothing  filter that effectively  reduces their angular resolution and  thus the
expenditure of degrees of freedom.  For example, we can leave the number of bins at 8 (or at
16 for that matter) and instead impose:

       Bias      = [Eps2] . <{C(k-l) - 2C(k) + C(K+1)}2>                         [8]

The righthand side of [8] is  the average over  the 8 (or 16) sectors of the squared curvature of
the angular distribution, with circular  boundary conditions.  In the limit as Eps  is large,
minimizing equation [1] forces the angular distribution function A(k,j) into a circle (	
but no azimuthal degrees of freedom have been spent on it).  In the limit as EPs  is small
minimizing  [1]  may  induce  interesting  garbage by  information bankruptcy.   At  some
intermediate  Eps may lie an optimum  tradeoff  for  maximum resolution consistent with the
information budget.

Shuffle

Finally, every regression should be tested with nonsense. Tracer-rose permits users to shuffle
the input  tracer file and to  generate nonsense inversions whose bumps and wiggles help to
inoculate the user from premature and misplaced enthusiasm.

Summary

To summarize the use of tracer-rose:

       a.     Data are files of daily concentration  measurements and  of hourly winds and
              directions.

       b.     Select a number of azimuthal fins (usually 8 or 16).

       c.     Choose either "natural" or "isotropic"  weights.

       d.     Elect to bias or not,  through a choice  of Eps.
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Tracer-rose then turns the crank and generates:

       a.     A polar diagram of source attributions, as a function of wind directions, with
              superimposed standard deviations, corrected for degrees of freedom.

       b.     A daily modulation function and a meander velocity.

       c.     The constant C3, which can be related to spatial and mixing coefficients.

       d.     A set of Ymod(i) that can be compared with observations.  The V of equation
              [1]  is a score for this comparison.

       e.     A set of regression coefficients that can be used with new winds and directions
              to estimate new Ymod(i). In particular, they may be used to estimate the effect
              of new winds  on  the  statistics of Ymod.  For example, what would be the
              exceedances to be expected with data from longer wind records, for which the
              concentration measurements are missing?
Then
       f.     Shuffle the tracer observations, to test significance.

Results

First, tracer-rose has been used with WV3 and 77 days of real winds  (Fire Station No. 12, fall
and winter of 1985)  and a synthetic pattern of three stacks, S, and one receptor, X, as follows:

                            s     o     o      o     s

                            o    o     o      o     o

                            O    O     X      O     O

                            00000

                            S     O     O      O     O     < -  note missing stack

With these winds  and sources WV3 generated a sequence of modeled 24-hour averaged tracer
concentrations, at  X. Tracer-rose then turned this process around with the synthetic tracers and
the real winds to try to reproduce the input stack pattern.

Figure 1 shows a  tracer-rose resulting from 16 azimuthal bins, with isotropic weights, and no
bias.  The three lobes in the central  dark  curve are clear, but note  the large standard errors
shown in the inner and outer lighter curves, which are displaced by minus and plus one standard
deviation.  Reasons  for this are discussed in the preceding section.

Figure 2 shows the same inversion,  slightly biased to minimize the average curvature.   The
three-lobe pattern  barely survives, and the outer curve has shrunk a bit.

Figure 3  shows a scattergram of tracer concentrations from WV3, labeled  "observations",
plotted against those from tracer-rose, labeled "model".  The robust  MRE of this comparison
is less than 10 percent.

Tracer-rose  also  recovered  a meander velocity  (0.70  ±0.11 m/s) and  daily  modulation
coefficients (Cl = C2 = -0.50 ± 0.11) that compare reasonably with those of WV3 (0.50 m/s,
-0.69, and -0.36).


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These  results encourage that  tracer-rose works,  but emphasize the cruel economics of
information demand.  To ease the crunch, more data are needed.

Figure 4 shows results from tracer-rose with 355 nondefault PM10 measurements, and 8520
hourly wind directions and velocities, at Fire Station No. 12, in 1986.  The presentation of the
error curves has been  changed  here, and some extra target circles eliminated to minimize an
otherwise an otherwise too busy display.  The inner thin circle now shows the isotropic part of
the azimuthal distribution, and the outer thin curve shows the  "plus  one sigma"  standard
deviations.   These are not concentric with the isotropic circle, owing to  the differing  numbers
of hours with the winds in the various sectors.

Examination of the dense curve in Figure 4 reveals a 3-sigma projection towards the southeast,
(Kaiser?),  and  two  1-sigma  bumps  towards the  northwest,  (Simpson?), and southwest
(unknown). WV3 also shows a maximum in surface PM10 concentrations to the southeast of
Fire Station No.  12,  largely from fugitive emissions attributed to Kaiser.  WV# perhaps
exaggerates these  from too-severe local boundary conditions that have been assigned  to the
terrain north of Kaiser.  On the other hand,  tracer-rose's  finger-point towards Kaiser (rather
than nearer Simpson plant) is consistent with what WV3 has been trying tell us.

Figure 5 displays  the  scattergram of Ymod  (ordinate) vs Yobs (abscissa) for this regression.
Note that,  as with WV3, tracer-rose underpredicts the higher observations.   The MRE  scores
for tracer-rose and WV3 nearly identical.

As remarked above, regressions  should be tested with nonsense.   Figures  6 and 7 display a
polar diagram and scattergram  after a random  shuffle of the sequence of PM10 observations.
One lobe in Figure 6 touches the 1-sigma curve at the southwest.  With 16 independent angular
bins the odds would be about 16:6 that one bin would exceed 1-sigma.  Owing to the bias term,
the bins are not independent, however, and the  odds that any single bin would exceed 1-sigma
are reduced approximately to 1:1.  Thus, the observed single lobe at 1-sigma is consistent with
random chance. The flat scattergram of Figure 7 shows no greater skill than would a Farmers'
Almanac.

Finally, for this brief report, angular distribution plots of the PSAPCA's  source inventory have
been examined and displayed with Fire Station No. 12 at the center and weighted with various
inverse powers of the radial distances.  With r^  weights (plausible  if vertical mixing is
suppressed) these  plots tend to emphasize the  Simpson plant, rather than  Kaiser.  With i*~5
weights  (plausible if  vertical diffusion  operates efficiently) they emphasize the very near
sources.

Questions

Its early, yet, and  tracer-rose needs more testing.  A very long data set would be informative.
The model can handle two years without modification, and with tricks could perhaps do four.
Chemically segregated data (a  metal tracer,  for example,  and not just PM10) should enhance
signal-to-noise.  Data  near to a single strong stack (Centralia) would help verify the variance
calculations.
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APPENDIX H.  SUPPORTING DOCUMENTS
      1)    Ellenson, W.D. Data Report for the Puget Sound Air Toxics
           Deposition Study.  NSI Environmental Services, Research Triangle
           Park, NC.

      2)    NBA, Inc.  Tacoma Simpson Kraft Source Testing Analytical
           Report, submitted to Puget Sound Water Quality Authority,
           March 1990.

      3)    NBA, Inc.  Simpson Tacoma Kraft Emission Testing, Size-
           Segregating Dilution Sampling Report, submitted to Puget
           Sound Water Quality Authority, April 1990.
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