ML19261C756
| ML19261C756 | |
| Person / Time | |
|---|---|
| Site: | Crystal River  |
| Issue date: | 03/31/1979 |
| From: | FLORIDA POWER CORP. |
| To: | |
| Shared Package | |
| ML19261C755 | List: |
| References | |
| NUDOCS 7904020131 | |
| Download: ML19261C756 (600) | |
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{{#Wiki_filter:ANN'J AL ENVIRONMENTAL OPERATING REPORT VOLUME 1 - NONRADIOLOGICAL 1/1/78 - 12/31/78 CR(STAL RIVER - UNIT 3 FLORIDA POWER CORPORATION FACILITY OPERATING LICENSE NO. DPR-72 DOCKET NO. 50-302 March, 1979 O oW 6 Bright ( AERVoll) D62
TABLE OF CONTENTS PAGE I Introduction 1 II Maximum Delta T Across Condenser 3 III Maximum Discharge Temperature 4 IV Chemical 5 V Annual Record of Metabolism of Estuarine Ecosystems 6 VI Community Structure Study 7 VII Impingement of Finfish and Shellfish 8 VIII Chemical industrial Waste Water Treatment System 9 APPENDICES I Community Structure Study II Annual Record of Metabolism of Estuarine Ecosystems e Bright (AERVoll) D62
I. INTRODUCTION The Nonradiological Environmental Monitoring Program et Crystal River Unit 3 is designed to determine any significant ervironmental effects due to power operation, particularly unpredicted and catastrophic changes. A preoper-ational program was designed and performed to serve as a baseline for com-parison with operational data. Using this baseline and the plant design parameters, Limiting Conditions for Operation were developed. Operation within these LCO's will reduce the plant's effect on the environment to a minimal level. This will be confirmed by the Nonradiological Surveillance Program. It is recognized that a period of adjustment is expected concur-rent with the plant's initial operation. Therefore, it may not be possible to draw any conclusions from the data in this report unless the data is similar to the preoperational data. In that case, the plant did not affect the environment to the extent that a period of adjustment was experienced and that part of the environment may be assumed to be at its stablilzed level. Each of the Nonradiological umiting Conditions for Operation will be addressed and evaluated separately. Because of the extent of work required to perform the Nonradiological Surveillance Program, some sections of it were contracted out to consultants. The sections which were divided among consultants are delineated in Table 1-1. The reports from these consultants are complete in themselves and are inserted in this report as Appendices. 9 TABLE I-1 Consultant Research ET5 Section University of Florida Productivity and respiration 3.1.1 Dr. H.T. Odum in discharge area Productivity, respiration and 3.1.2 biomass in discharge marsh Oxygen measurements in outer bay 3.1.4.a Oxygen measurements in canals 3.1.4.b Stem counts of marsh grass 3.1.4.e Connell Metcalf and Eddy Diversity and biomass in dis- 3.1.1 charge area Zooplankton samples, outer bay 3.1.*.a Monitor seagrass condition 3.1.4.c Oyster reef quadrat counts 3.1.4.d 6 II. MAXIMUM DELTA T ACROSS CONDENSER At Crystal Riier Unit 3, the temperature rise across the condenser should nM exceed 17.5'F for more than three consecutive hours and should not ext. .d 21 F (Specification 2.1.1). This is based on design data showing t h a '. 2 temperature rise will be 17.5 F at capacity and on the three hours requ. :.o clean a condenser section. The monitoring requirements demand the use of RTD's in the inlet and outlet waterboxes that are monitored and alarmed by the plant computer. However, if the RTD's or computer is inoperative, local indication on the wat;rboxes must be used. During initial power ascension, the condenser AT reached 17.5 F before the plant reached 100f. power. Investigations lead to the dic;overy that the computer RTD's were in a "hotspot" in the outlet water boxes and thus represent an overly conservative reading of the condenser outlet temperature. On March 31, 1977, the RTD's were declared inoperable and local indications used to determine the condenser AT. It is desirable to have the computer logging and alarming the condenser AT instead of doing it manually. Further investigations resulted in finding a position in the discharge piping for a computer RTD that has a relatively flat themal profile. This modification is being pursued. The condenser AT did reach 17.5 F during 1978 but on each occasion thermal power was reduced and the aT was reduced to <17.5 F in less than three hours. The limit of 17.5 F was never exceeded for more than three hours and 21 F was never exceeded. Beacuse of constantly changing plant condi-tions throughout the year, it is inappropriate to attempt a statistical
! valuation of the condenser AT. In general, though, a condenser aT of about 17 F using local indicators was the average at full power.
9 III. MAXIMUM DISCHARGE TEMPERATURE The temperature of the once-through cooling water discharged from the Crystal River Energy Center to the Gulf of Mexico should not exceed 103 F for more than three consecutive hours and should not exceed 106 F. These limits are based on the aT specification on the Maximum ai Across Conden-ser, on the design condenser AT's for Units 1 and 2, and on an assumed max-imum ambient water temperature of 87 F. (The maximum ambient temperature ever recorded is 92 F and the mean value of the maximum ambient temper-atures recorded for July from 1945 to 1962 is 89.3 F.) The temperature monitoring system is a computer-controlled radio link to the sensor bouys. When this system becomes inoperable, the discharge tem-perature is estimated from the flow-weighted average of the condenser dis-charge temperatures or by actual temperature measurement at the Point of Discharge. The discharge temperature to the Gulf of Mexico did not exceed 103 F during 1978. A statistical evaluation of the discharge temperatures to the Gulf of Mexico is inappropriate because of the constantly changing thermal condi-tions of the three units at Crystal River. O IV. CHEMICAL Environmental Technical Specification 2.3.1 limits the amount and concen-tration of total residual chlorine in the discharge as the result of chlor-ination of the co:Jenser water boxes. This chlorinaticn is designed to inhibit the growth of marine organisms in the condensers. Due to the employment of mechanical means of cleaning the condensers, chlorination was not required during this reporting period. Environmental Technical Specification 2.3.2 prohibits the use of chromates as corrosion inhibitors in the circulating water system. No chromates were used as corrosion inhibitors in the circulating water system during the period of this report. 8
'v . ANNUAL RECORD OF METABOLISM OF ESTUARINE ECUSYSTEMS The annual record of metabolism of estuarine ecosystems at the Crystal River site as required by Specifications 3.1.1, 3.1.2, and 3.1.4 (see Table I-1) was conducted by the Department of Environmental Engineering Sciences, University of Florida. The data for the quarterly samples is in Appendix II as well as the analyses and conclusions.
Two Licensee Event Reports (LERs) were submitted to the Commission. LER 78-026/04L-0 was the result of a difference of more than two standard deviations between the preoperational study and the operational study of the animal abundance of the benthic system. LER 79-021/04L-0 was the result of that same difference in the salt marshes for live biomass, dead biomass, and gross productivity. 9 VI. COMMUNITY STRUCTURE STUDY The cc::inunity structure study at the Crystal River site as required by Specifications 3.1.1 and 3.1.4 (see Table I-1) was conducted by Connell Metcalf and Eddy. The data for the quarterly samples is in Appendix I as well as the analyses and conclusions. i 9 VII. IMPIriGEftEtiT OF FINFISH AliD SHELLFISH The impingement study at the Crystal Piver Site, as required by Specifica-tion 3.1.3, was conducted by the fiUS Corporation. The first year of the study was concluded on March 15, 1978 due to the impendinq dredging to be performed in the intake canal . This was allowed by License Amendment tio. 12 issued on January 23, 1978. A report of the full year's worth of study data, " Crystal f.ive Unit 3 Impingement Report, March 13, 1977 to March 13, 1978," was forwai ded to the Staf f on August 30, 1978; therefore data for January 1 through March 13 will not be presented here. Upon approval of the impingement report by the Staf f, the impingment speci-fication may be discontinued. The following Licensee Event Reports were submitted to the Commission due to weekly samples with fish and shellfish biomass of greater than 50 kilograms: 78-001/04X-0 78-002/04X-0 78-003/04X-0 78-005/04X-0 78-007/04X-0 78-007/04X-0 78-009/04X-0 78-010/04X-0 78-011/04X-0 O VIII. CHEMICAL / INDUSTRIAL WASTE WATER TREATMENT The monitoring of the Chemical / Industrial Waste Water is performed to determine if the waste water is controlled so as to not adversely affect public health or the natural aquatic environment. All required samples were collected and analyzed for the required parmeters (Table VIII-l through 5 and 7) except for the Well No. 5 in April' all samples in May; and Well No. 5 in December for Phosphate. The non-collections for Well No. 5 in April and May were reported in LER 78-16/04L-0, dated May 31, 1973; and the ron-collection of all samples in May, except Well No. 5, was reported in LER 78-17/04L-0, dated June 14, 1978. These non-collections are reported as "NC/M" (not collected / measured) in the surm'ary tables. The Phosphate sample for Well No. 5 in December was contaminated. In addi-tion, the West Pond was dry in April. Samples were also drawn from the in-take canal directly to the south of the waste water ponds (Table VIII-6). The Minimum Detectable Level (MDL) of each p?rameter for the samples is in Table VIII-8. In addition to the reporting of rcsults, the tables also list the mean, the 195% confidence boundaries (defined as i 1.960) and the range of each para-meter for each sample location. For the purposes of statistics, all values that were reported as "<MDL" were assumed to be one-half of their MDL. The statistics for the pH values were performed on the values themselves even though pH is the negative logarithm of the hydrogen ion concentration. In four cases, the same parameter was outside the 195% confidence limit for a pond and an outside sample location for the same sample period. These were iron for the East Pond and Well No. 5 in June; copper for the East Pond and Well No.1 in September, dissolved solids in the West Pond and Well No.1 in September; and nitrate for the West Pond and Well No. 4 in December. Over the reporting period, seven parameters of the two ponds were outside the 195% confidence boundaries, nine parameters for the three wells, and the two canals had five parameters outside the limit. In 1976 (preoperational) and 1977 (operational), the number of pararreters exceeding the 195% confidence limits were twenty-four and twenty-six respectively. Both 1976 and 1977 each had one sample period in which the same parameter exceeded the 195% confidence limit for a well and a pond. 9 TABLE Vill-1 MONTitLY CilEMICAL-INDUSTRI AL UASTE WATER POND ANALYSIS Sample Location No.1 - East Pond Dissolved Hitrate Phosphate Sulfate Iron Cop per Zinc Oate Solids (NO3 ) (PO4 ) (S04 ) (Fe) (Cu) (Zn) Sampl ed pH (mg/1-TDS) (mg/1-N) (mg/1-P) (mg/1-SO4 ) (mg/1-Fe) (mg/1-Cu) (mg/1-In) l-11-78 3.01 6,526 0.13 1.60 1,800 29.0 0.18 0.09 2-7-78 3.7 2,535 1.36 0.05 1,600 2.53 0.21 0.09 3-7-78 3.0 1,370 0.86 0.40 500 4.87 0.23 0.09 4-4-78 2.4 4,550 2.0 3.20 1,475 18.0 0.33 0.30 [ o NC/M NC/M NC/M NC/M NC/M NC/M NC/M hC/M i 6-6-78 3.5 1,960 0.42 0.10 1,550 134 0.73 0.57 7-12-78 2.6 1,790 1.10 17.5 875 6.1 0.40 0.38 8-15-78 9.2 8,780 0.16 2.7 100 0.58 0.18 0.04 9-13-78 6.7 1,450 <MOL 0.80 2,380 34 1.76 0.61 10-11-78 9.1 1,360 0.20 0.10 775 3.44 0.05 0.0/ 11-15-78 9.9 1,090 0.16 0.10 275 0.40 0.12 0.05 12-13-78 7.9 1,580 0.3? 0.20 1,125 2.73 0.10 0.20 Mean 5.55 3,090.09 .67 2.43 1,132.27 21.42 0.39 0.23
~+ 951 Con-fidence 5.91 4,888.39 .67 2.43 1,373.06 76.71 0.96 0.41 Range 2.6/9.9 1,090/8,780 .13/2.0 .05/17.5 100/2,380 .4/134 .05/1.76 .04/.61
TABLE VIII-2 Mo'PHLY CilEMICAL-IrlDUSTRIAL WASTE WATER P0f4D ANALYSIS Sample Location No. 2 - West Pond Dissolved Nitrate Phosphate Sulfate Iron Copper Zinc Date Solids (NO3 ) (PO4 ) (SO4 ) (Fe) (Cu) (Zn) Sampled pil (mg/1-TDS) (mg/1-N) (mg/1-P) (mg/1-SO4 ) (mg/1-Fe) (mg/1-Cu) (mg/1-Zn) l-11-78 2.57 3,438 1.39 1.40 1,225 12.0 0.28 0.16 2-7-78 3.13 2,405 1.72 0.20 1,350 2,84 0.17 0.14 3-7-78 3.1 1,770 1.69 0.45 775 7.70 0.32 0.14 4-4-78 Dry Dry Dry Dry Dry Dry Ury Dry NC/M NC/M NC/M NC/M NC/M NC/M NC/M NC/M i 6-6-78 3.5 2,150 0.40 (MDL 1,750 67. 0.27 0.66 7-12-78 2.4 2,960 1.91 3.00 1,200 3.53 0.78 0.36 B-15-78 9.5 1,450 0.31 1.6 175 0.50 0.09 0.08 9-13-78 7.5 4,570 0.40 0.85 2,150 11. 0.70 0.41 10-11-78 5.1 1,690 0.26 <MDL 600 42.3 0.16 0.39 11-15-78 11.I 1,180 0.08 0.60 150 0.57 0.06 0.02 12-13-78 9.2 1,400 6.61 1.40 900 1.91 0.12 0.06 Mean 5.73 2,301.30 1.48 1.19 1,027.50 14.94 0.30 0.24 195% Con-fidence 6.45 2,102.57 3.80 1.74 1,259.14 43.32 0.49 0.40 Range 2.4/11.1 1,180/4,570 0.08/6.61 0.2/3.00 150/2,150 0.50/42.3 0.06/0.78 0.02/0.66
TABLE Vill-3 MONTHLY CliEMICAL-INDUSTRI AL WASTE WATER POND ANALYSIS Sample. Location No. 3 - Well No. 1 Dissolved Nitrate Phosphate Sulfate Iron Copper Zinc Oate Solids (NO3 ) (PO4 ) (SO4 ) (Fe) (Cu) (Zn) Sampl ed pH (mg/l-TDS) (mg/1-N) (mg/1-P) (mg/1-504 ) (mg/1-Fe) (mg/1-Cu) (mg/1-Zn) l-11-78 7.71 10,010 0.61 0.30 1,300 1.72 0.02 0.04 2-7-78 7.4 9,360 0.31 0.20 1,375 0.58 0.03 0.00 3-7-78 7.6 8,160 0.03 0.30 1,230 0.71 0.02 0.04 4-4-78 7.1 8,710 0.18 0.35 1,250 0.47 0.62 0.17 [ NC/M NC/M NC/M NC/M NC/M NC/M NC/M NL/M N i 6-6-78 7.0 7,280 0.05 0.20 1,230 1.43 <MDL 0.03 7-12-78 7.0 7,900 0.05 0.30 1,200 1.30 0.02 0.15 8-15-78 7.7 7,740 0.02 0.3 1,250 1.39 <MDL 0.03 9-13-78 6.9 11,500 <MDL 0.10 2,030 38. 0.18 0.76 10-11-78 7.3 7,860 0.24 0.15 1,150 3.95 0.02 0.0/ 11-15-78 7.8 6,450 0.11 0.25 1,130 3.24 0.04 0.09 12-13-78 7.4 7,050 0.11 0.15 1,200 7.7 0.04 0.41 Mean 7.36 8,3/4.55 0.171 0.24 1,304.09 5.50 0.04 0.17 1 95% Con-fidence .63 2,846.31 0.36 0.16 489.82 21.53 0.10 0.44 Range 6.9/7.8 6,450/11,500 0.02/0.61 0.10/0.35 1,120/2,030 0.47/38.0 0.02/0.18 0.03/0.76
TA8LE Vill-4 MONillLY CHEMICAL-If4DUSTRI AL WASTE WATER POND ANALYSIS Sample Location No. 4 - Well No. 4 Dissolved Nitrate Phosphate Sulfate Iron Cop per Zinc Oate Solids (NO3 ) (PO4 ) (SO4 ) (Fe) (Cu) (Zn) Sampled pil (mg/1-T05) (mg/l-N) (mg/1-P) (mg/1-SO4 ) (mg/1-Fe) (mg/1-Cu) (mg/1-Zn) 1-11-78 7.37 10,140 0.10 0.50 5,000 5.28 0.06 0.01 2-7-78 7.1 11,570 0.04 <MDL 6,800 3.56 0.06 0.04 3-7-78 7.1 13,460 0.10 0.10 10,200 1.10 0.60 0.04 4-4-78 7.1 11,900 0.05 0.40 9,200 1.41 0.06 0.15 [ NC/M flC/M NC/M NC/M NC/M NC/M NC/M NC/M us i 6-6 ~d 6.7 7,800 0.06 0.10 6,100 9.7 0.01 0.01 7-12-78 6.8 7,420 0.08 <MDL 5,800 12.8 0.04 0.11 8-15-78 7.2 10,800 0.02 0.2 10,500 6.1 0.07 0.03 9-13-78 7.1 5,030 <MDL 0.05 3,200 47 0.05 0.22 10-11-78 7.0 6,030 0.10 0.05 5,000 39.9 0.01 0.04 11-15-78 7.1 3,960 0.02 0.05 3,200 19 0.03 0.08 12-13-78 7. 5 5,160 0.35 0.05 4,000 7.8 0.04 0.25 Mean 7.10 8,479.11 0.09 0.17 6,272.73 13.97 0.04 0.09
~+ 95% Con-fidence 0.44 6,354.96 0.19 0.33 5,173.87 30.46 0.04 0.16 Range 6.7/7.5 3,960/13.460 0.02/0.35 .05/0.5 3,200/10,500 1.10/39.9 0/01/0.0/ 0.01/0.25
TABLE VIII-5 MONTHLY CliEMICAL-INDUSTRIAL WASTE WATER POND ANALYSIS Sample Location fio. 5 - Well fio. 5 Dissolved Nitrate Phosphate Sulfate Iron Copper Zinc Date Solids (NO3 ) (PO4 ) (S04 ) (Fe) (Cu) (Zn) Sampl ed pH (mg/1-TDS) (mg/1-N) (mg/1-P) (mg/1-504 ) (mg/1-Fe) (mg/1-Cu) (mg/1-Zn) 1-11-78 6.99 15,795 0.05 0.60 1,920 0.20 0.06 (Mut 2-7-78 6.8 14,235 0.62 0.35 1,800 0.21 0.04 0.05 3-7-78 6.8 15,670 <MDL 0.40 1,800 0.07 0.03 0.02 NC/M f4C/M flC/M NC/M fiC/M NC/M flC/M NC/M NC/M NC/M I4C/M NC/M flC/M f1C/M f4C/M NC/M i 6-6-78 6.7 9,300 0.06 0.05 1,550 43 <MDL 0.05 7-12-78 7.1 4,040 <MDL <MDL 775 0.39 0.03 0.09 8-15-78 7.0 6,510 <MDL 0.1 1,580 20 0.02 0.01 9-13-78 7.0 4,320 <MDL 0.10 1,230 13 0.02 0.02 10-11-78 7.1 3,650 0.02 <MDL 1,030 26.2 <MUL 0.10 11-15-78 7.3 3,090 0.02 <MDL 975 3.03 0.02 0.23 12-13-78 7.2 3,520 0.02
- 1,000 2.19 0.02 1.20 Mean 7.00 8,013.00 0.03 0.27 1,366.00 10.83 0.03 0.20 1 95% Con-fidence 0.37 10,427.75 0.04 0.43 808.34 28.82 0.03 0.75 Range 6.7/7.3 3,090/15,795 0.02/0.06 0.05/0/60 775/1,920 .07/43 .02/.06 .01/1.20
- Contaminated
TABLE Vill-6 MONTHLY CHEMICAL-IflDOSTRIAL WASTE WATER POND AtlALYSIS Sample Location flo. 6 - Intake Canal Dissolved Nitrate Phosphate Sulfate Iron Cop per Zinc Date Solids (NO3 ) (P04 ) (SO4 ) (Fe) (Cu) (Zn) Sampl ed pil (mg/1-TDS) (mg/1-N) (mg/1-P) (mg/1-SO4 ) (mg/1-Fe) (mg/1-Cu) (mg/1-Zn) l-11-78 8.25 22,750 <MDL <MDL 1,750 0.22 0.05 0.03 2-7-78 8.1 21,450 <MDL <MDL 1,625 0.28 0.05 0.05 3-7-78 8.0 19,110 0.02 0.05 1,350 0.10 0.05 0.09 4-4-18 7.6 17,940 0.02 0.40 1,375 0.15 0.03 0.05 f4C/M fiC/M NC/M NC/M NC/M NC/M NC/M NC/M G . 6-6-78 7.7 20,500 0.02 0.15 1,550 0.19 0.02 0.05 7-12-78 7.9 23,410 <MDL 0.20 1,875 0.25 0.05 0.15 8-15-78 8.1 21,300 <MDL 0.2 1,630 0.10 0.04 0.19 9-13-78 7.9 26,900 <MDL 0.20 2,330 0.24 0.06 0.13 10-11-78 7.8 26,000 (MDL 0.20 2,250 0.26 0.05 0.07 11-15-78 8.0 22,900 <MDL 0.20 1,400 0.31 0.05 0.06 12-13-78 6.8 23,730 0.02 0.10 600 0.38 0.06 0.06 Mean 7.83 22,362.73 0.02 0.19 1,612.27 0.23 0.05 0.08 1 95% Con-fidence 0.75 5,288.17 0.0 0.19 921.20 0.17 0.02 0.10 Range 68/8.25 17,940/26,900 0.0/0.02 0.05/0.40 600/2,330 0.10/0.38 0.02/0.06 0.03/0.19
TABLE Vill-7 MONTHLY CHEMICAL-IfiDOSTRI AL WASTE WATER POND Af4ALYSIS Sample Location No. 7 - Discharge Canal Dissolved fli t rate Phosphate Sulfate Iron Copper Zinc Date Solids (f403 ) (PO4 ) ($04) (Fe) (Cu) (in) Sampl ed pH (mg/1-TDS' , (mg/'-4) (mg/1-P) (mg/1-SO4 ) (mg/1-Fe) (mg/1-Cu) (mg/1-Zn) l-11-78 8.27 22,950 <MDL <MDL 1,750 0.27 0.05 0.02 2-7-78 8.1 20,475 < f4DL <MDL 1,625 0.37 0.uS 0.05 3-7-78 8.0 19,500 0.02 0.05 1,380 0.11 0.05 0.12 4-4-78 1' 18,980 0.03 0.30 1,3/5 0.12 0.03 0.07 NC/M f4C/M f4C/M HC/M fiC/M flC/M NC/M fiC/M 5' . 6-6-78 7.7 21,500 0.02 0.15 1,730 0.20 0.02 0.07 7-12-78 8.0 23,860 <MDL 0.20 1,975 0.31 0.05 0.17 8-15-78 8.1 iz,200 (MDL 0.2 1,780 0.11 0.04 0.04 9-13-78 7.9 26,900 (MDL 0.20 2,330 0.25 0.06 0.04 10-11-78 7.9 26,300 <MDL 0.20 2,250 0.27 0.04 0.05 11-15-78 8.1 23,100 <MDL 0.20 1,530 0.35 0.02 36 12 '3-78 7.1 24,770 0.02 0.10 1,875 0.26 0.06 0.0/ Mean 7.89 22,775.91 0.02 0.18 1,781.82 0.24 0.04 3.34
-+ 95% Con-fidence 0.63 5,077.45 0.01 0.14 614.94 0.18 0.03 21.23 Range 7.1/8.27 18,980/26,900 0.02/0.03 0.05/0.30 1,375/2,330 0.11/0.37 0.02/0.06 0.02/36.0
TABLE VIII-3 MINIMUM DETECTABLE LEVELS Parameter MUL pH 0.001 Dissolved Solids 0.7 mg/t Nitrate 0.02 mg/t Phosphate 0.01 mg/t Sulfate 3 mg/ t Iron 0.01 mg/t Copper 0.01 mg/ t Zinc 0.01 mg/t 0 APPEi4 DIX I
~OMMUtilTY STRUCTURE STUDY O
Bright (AERVoll) 062
CRYSTAL RIVER COMMUNITY STRUCTURE STUDY FOR FLORIDA POWER CORPORATION ANNUAL REPORT 1978 O
TABLE OF CONTENTS Item Page No. TABLE OF CONTENTS i LIST OF TABLES iii LIST OF FIGURES vi
SUMMARY
xi INTRODUCTION I-l MATERIAIS AND METHODS I-6 Field Operation I-6 Bottom Core Samples I-6 Venturi Samples I-6 Benthic Plant Samples I-7 Seagrass Monitoring I-8 Oyster Reefs I-8 Zooplankton Samples I-9 Environmental Parameters I-10 Laboratory Operation I-ll Quality Control review I-ll Bottom Core Samples I-12 Venturi Samples I-12 Benthic Plant Samples I-13 Oyster Reefs I-14 Zooplankton Samples I-14 Voucher Collection I-15 RESULTS I-16 General Comments I-16 Benthic Animals I-39 General Treatment 1 39 Total Animal Benthos I-43 Polychaetes I-61 Crustaceans I-69 Mollusks I-71 Other Groups I-73 Seagrass and Macroalgae I-76 Macroalgae I-76 Seagrasses I-76 i
Item Page No. Seag rass Monitoring I-81 Inside Radials I-81 Outside Trans~ ts I-103 Oyster Reefs I-123 Oysters I-123 Oyster Spat I-125 Other Mollusks I-127 Crustaceans I-129 Z ooplank ton I-130 Grouped Data Sumsationa I-135 COMPARISONS WI'III PRE-OPERATIONAL DATA I-140 DISCUSSIONS AND CONCLUSIONS I-160 REFERENCES CITED I-165 APPENDIX A I-A-1 APPENDIX B Table B-1. Basic stati~ tics for each taxon and wet and dry wei :its for each major group from botton. ; ore samples of 1978. I-B-1 Table B-2. Basic st,tistics for each taxon and wet and dry mights for each major group f rom ver. turi suction samples of 1978. I-B-43 Table B-3. Diversit/ and evenness for each benthic and zoo;1ankton station for 1978. I-B-81 Table B-4. Basic si stiscies on taxon abundance and total dry :1ghts of zooplankten samples of 1978. I-B-86 Table B-5. Basic stat 1stice on inside control and discharae adials for 1978. I-B-123 Table B-6. Basic sta;istics on outside control and discharge transects for 1973. I-B-144 ii
LIST OF TABLES Item Page No. Table 1. Taxonomic list and relative occurrence of benthic organisms (excluding organisms found only on oyster reefs) in the vicinity of Florida Power Corporation's Cyrstal River Plant. I-17 Table 2. Taxonomic list and relative occurrence of benthic organisms on oyster reefs in the vicinity of Florida Power Corporation's Crystal River Plant. I-27 Table 3. Taxonomic list and relative occurrence of zooplankton in the vicinity of Florida Pover Corporation's Crystal River Plant. I-29 Table 4A. Results of regression analycis of benthic population parameters on physical parameters for the control and discharge basins. Data are from the venturi samples of different sampling periods of 1978. I-59 Table 4B. Results of regression analysis of benthic population parameters on physicsl parameters for the control and discharge basins. Data are from the bottom core samples of different sampling periods of 1978. I-60 Table 5. Mean biomass (grams dry weight) m -2 of major benthic groups other than annelids, arthropods, and mollusks in control and discharge basins for different sampling periods of 1977. I-75 Table 6. Mean biomass (grams dry weight) m-2 of seagrasses (SG) and macroalgae (MA) at discharge (D) and control (C) stations during different sampling periods of 1978. I-78 Table 7. Mean percent cover of seagrasses m-2 along two inside control radials and three inside discharge radials for different sampling periods of 1978. I-82 Table 8A. Mean percent cover seagrasses m-2 along outside control transects for June, September and December sampling periods of 1978. I-104 Table 8B. Mean percent cover seagrasses m-2 along outside discharge B transects for June, September and December sampling periods of 1978. I-105 Table 8C. Mean percent cover seagrasses m-2 along outside discharge C transects for June, September and December sampling g periods of 1978. I-106 111
LIST OF TABLES ITEM PAGE NO. Table 8D. Mean percent cover seagrasses m-2 al ng outside discharge D transects for June, September and t *eember sampling periods of 1978. I-108 Table ?. Major zooplankton groups and mean numb; 3 m-3 for day, night, surface, and mid-depth tows. I-132 Table 10. Annual mean biomass (g m-2 except zocolankton m-3) for control and discharge basins,1977 and 1978. I-136 Table 11. Annual mean abundance m-2 (zooplankten m-3) for control and discharge basins, 1977 --d 1978. I-137 Table 12A. _Mean annual benthic animal and zoeplankton diversity (H) and evenness (e) for control and discharge basins, 1977 and 1978. I-138 Table 12B. Mean benthic animal diversity (5) au ! evenness (e) for seasonal periods in control and discharge basin 3, 1977 and 1978. I-138 Table 12C. Total zooplankton diversity (E) and evonness (e) at control and discharge stations, June and Decent-1977 and 1978. I-138 Table 13. Results of t statistic for difference between control and discharge means for each sampling par ted of 1978. I-139 Table 14. Mean macrophyte biomass (g dry wt.) m -2 by taxon, sampling period and basin for pre-operational and post-operational (1977, 1978) studies. I-142 Table 15. Mean diversity by taxon, sampling period and basin for pre-operational, 1977 and 1978 studies. I-146 Table 16. Comparative oyster reef data for pre-cpt rational, 1977 and 1078 studies for summer and winter sampli ng periods. Data presented are for 0.25 m2 quadrats. I-147 Table 17A. Overall benthic community paramet: , -2 from venturi samples and temperature and salinity for the contrcl basin from pre-operational and 1977 and 1978 studies. I-149 Table 17B. Overall benthic community parameters r -2 from venturi samples and temperature and salinity for the discharge basin from pre-operational and 1977 and 1978 studies. I-150 O iv
LIST OF TABLES ITEM PAGE NO. Table 18. Results of the t statistic for dif ferences between the pre-operational mean ( a 1) and the post-operational mean (U 2) for abundance and biomass from venturi samples and for temperature and salinity. I-152 O v
LIST OF FIGURES Item Page Mc. Fig. 1. Map of project area showing oyster reef stations and zooplankton stations. I-3 Fig. 2. Map of project area showing inside radials for seagrass monitoring and benthic sampling stations. I-4 Fig. 3. Map of project area showing outside transects for seagrass monitoring. I-5 Fig. 4. Temperature with T indicated at instae stations of control and discharge basins for different sampling periods of 1978. I-36 Fig. 5. Salinity with S indicated at inside stations of control and discharge basins for diff, rent sampling periods of 1978. I-38 Fig. 6. Total number of taxa of polychrotes (6A) , crustaceans (6B), and mollusks (6C) at discharge and control stations for different sampling periods of 1978. I-42 Fig. 7. Mean abundance m-2 of animals collected in venturi samples in the control and discharge basins during 1978 sampling periods. I-45 Fig. 8. Mean abundance m-2 of annelids, mollusks, and crustaceans collected in venturi samples in the discharge (8A) and control (8B) basins during 1978 sampling periods. I-47 Fig. 9. Mean biomass m-2 of annelids, mollusks, and crustaceans collected in venturi samples in the control basin during 1978 sampling periods. I-48 Fig. 10. Mean biomass m-2 of annelids, mollusks, and crustaceans collected in venturi samples in the discharge basin during 1978 sampling periods. I-49 Fig, 11. Mean abundance m-2 of animals collected , bottom core samples in the discharge and control baains during 1978 sampling periods. I-50 Fig. 12. Mean annelid abundance m-2 collected in bottom core samples in the control and discharge basins during 1978 sampling periods. I-51 Fig. 13. Mean annelid biomass m-2 collected in bottom core samples in the control and discharge basins during 1978 sampling periods. I-52 Vi
LIST OF FIGURES Item Page No. Fig. 14. Species diversity spectra of benthic animals from venturi samples (14A) and bottom core samples (148) during 1978 sampling periods. I-55 Fig. 15. Evenness spectra of benthic animals from venturi samples (15A) and bottom core samples (15B) during 1978 sampling periods. I-57 Fig. 16. Regressions of annelid biomass (15A> and abundance (16B) on temperature for control and discharge basins. Data are unconverted station totals for bottom core samples of different periods in 1978. I-66 Fig. 17. Regressions of annelid biomass (17A) and abundance (17B) on salinity for control and discharge basins. Data are unconverted station totals for bottom core samples cf different sampling periods in 1978. I-68 Fig. 18. Mean macrophyte biomass m-2 in the discharge and control basins during 1978 sampling periods. I-79 Fig. 19. Mean leaf lengths for seagrasses at discharge stations (19A) and control stations (19B) for different sampling periods of 1978. I-80 Fig. 20. Distribution of Halophila engelmannii along inside radials of the control basin for March 1978. I-83 Fig. 21. Distribution of Halophila engelmannii along inside radials of the control basin for June 1978. I-84 Fig. 22. Distribution of Halophila engelmannii along inside radials of the control basin for September 1978. I-85 Fig. 23. Distribution of Halophila engelmannii along inside radials of the control basin for December 1978. I-86 Fig. 24. Distribution of Ruppia maritima along inside radials of the control basin for March 1978. I-87 Fig. 25. Distribution of Ruppia maritima along inside radials of the control basin for June 1978. I-88 Fig. 26. Distribution of Rupcia maritima along inside radials of the control basin for September 1978. I-89 Fig. 27. Distribution of Ruppia maritima along inside radials of the control basin for December 1978. I-90 vii
LIST OF FIGURES ITEM PACC NO. Fig. 28. Distribution of Syringodium filiforme along inside radials of the control basin for March 1978. I-91 Fig. 29. Distribution of Syringodium filiforme along inside radials of the control basin for June 1978. I-92 Fig. 30. Distribution of Syringodium filiforme along inside radials of the control basin for September 1978. I-93 Fig. 31. Distribution of Syringodium filiforme along inside radials of the control basin for December 1978. I-94 Fig. 32. Distribution of Italodule beau s lei along inside radials of the control basin for March 1978. I-95 Fig. 33. Distribution of !!alodule beaudettei along inside radials of the control basin for June 1978. I-96 Fig. 34. Distr ibution of IIslodule be iudettei along inside radials of the control basin for September 1978. I-97 Fig. 35. Distribution of Italodule beaudettet along inside radials of the discharge basin for March 1978. I-99 Fig. 36. Distr ibution of !!alodule beaudettei along inside radials of the discharge basin for June 1978. I-100 Fig. 37. Distribution of IIalodule beaudettei along inside radials of the discharge basin for September 1978 I-101 Fig. 38. Distribution of !!alodule beaudettei along inside radials of the discharge basin for December 1978. I-102 Fig. 39. Distribution of Halophila engelmannii along outside transects of the control and discharge areas for June 1978. I-lla Fig. 40. Dintribution of Italophila engelmannii along outside transects of the control and discharge areas for September 1978. I-lli Fig. 41. Distribution of !!alophila engelmannii along outside transects of the contro' 3 discharge areas for December 1978. I-ll2 Fig. 42. Distribution of Syringodium filiforme along outside transects of the control and discharge areas for June 1978. I-ll3 Viii
LIST OF FIGURES ITEM PAGE NO. Fig. 43. Distribution of Syringodium filiforme along ou tside transects of the control and discharge areas for Sep tember 1978. I-ll4 Fig. 44. Distribution of Syringodium i;1 tforme along ou ts ide transects of the control and discharge areas for December 1978. I-ll5 Fig. 45. Distribution of Halodule beaudettei along outside transects of the control and discharge areas for June 1978. I-116 Fig. 46. Distribution of Halodule beaudettei along outside transects of the control and discharge areas September 1978. I-ll7 Fig. 47. Distribution of Halodule beaudettei along outside transects of the control and discharge areas for December 1978. I-118 Fig. 48. Distribution of Thalassia testudinum along outside transects of the control and discharge areas for June 1978. I-119 Fig. 49. Distribution of Thalassia testudinum along outside transec ts of the control and discharge areas for September 1978. I-120 Fig. 50. Distribution of Thalassia testudinum along outside transects of the control and discharge area. for December 1978. I-121 Fig. 51. Raulo of mean biomass (adjusted to constant sample size of 230 oysters) to mean shell length of oysters greater than 2 cm in length at control and discharge oyster reef stations for different sampling periods of 1978. I-124 Fig. 52. Mean abundance m-2 (52A) and mean biomass m-2 (523) of oyster spat at control and discharge oyster reef stations for different sampling periods of 1978. I-126 Fig. 53. Mean abundance m-2 (53A) and tean biomass m-2 (53B) for other mollusks at control and discharge oyster reef stations for dif ferent sampling periods of 1978. I-128 Fig. 54. Mean abundance m-2 from venturi control samples of the pre-operational study superimposed ovat two standard deviations of the comparable mean from the 1978 study. I-153 Fig. 55. Mean abundance m-2 from venturi discharge samples of the pre-cperational study superimposed over two standard deviations of the comparable mean from the 1978 study. I-155 ix
LIST OF FIGURES ITEM PAGE NO. Fig. 56. Mean biomass m-2 from venturi control samples O of the pre-operational study superimposed over two standard deviations of the comparable mean from the 1978 study. I-157 Fig. 57. Mean biomass m-2 from venturi discharge samples of the pre-operational study superimposed over two standard deviations of the comparable mean from the 1978 study. I-159 O O
SUMMARY
The 1978 Final Report presents the results of the second year of the Unit 3 Technical Specifications study for Florida Power Corporation's Crystal River Power Plant. Benthic samples were collected during March, June, September and December 1978 and zooplankton samples were collec ted during June and December 1978. The benthic samples were taken from two inshore basins separated by a long jetty. The northern basin is the discharge area of the thermal effluent from the Crystal River Plant, while the southern basin is the control area. Zooplankton samples were taken several kilometers seaward of the respective basins. Beginnin, with the June 1978 sampling period, seagrass monitoring previously restricted to the inshore basins was extended to include extensive grids seaward of both inshore basins. The Crystal River Unit 3 was shut down on 3 Ma.ch 1978 and did not resume full operation until 29 September 1978. Results from this year's study probably reflect the absence of thermal effluent from this unit during the shutdown period. Both the control and discharge basins have changed h considerably in macrophyte composition and in macrophyte, xi
benthic animal (from venturi suction samples) and oyster abundence and biomass between the pre-operational and 1977-1978 studies. The control basin has experienced a proliferation of macroalgae and has shown an increase in macrophyte and venturi biomass as well as venturi and oyster abundance. The discharq basin, now categorized by a greater abundance of the seagrass Halodule beaudettei at the virtual exclusion of macroalgae, also had increases in total macrophyte and venturi biomass as well as venturi abundance. Oyster and spat abundance and biomass declined, however, in the discharge basin during this time. The major changes in discharge macrophyte composition and decrease in oyster and spat abundance and biomass between the pre-operational and 1977 studies could indicate a possible effect from Unit 3 operation. These O changes noted in the discharge basin were not apparent in the control basin. However, no significant differences in temperature or salinity were found between the pre-operational and 1977 or 1978 studies (Table 18; 1977 Final Report: Table 17). Differences between pre-operational and post-operational studies could be attributed to differences in sampling technique. It is not possible to attribute all of the apparent environmental alteration in the discharge basin, when compared with the control basin, to the effects of Unit 3 operation because the control and discharge basins were h xii
already quite different physical and biological systems before the commencement of Unit 3 operation. These differences, recorded at the outset of the 1977 study, were probably due to the combined effects of separation of the two basins by jetty construction, cutting and redirecting of tidal creeks, and the long term operation of the two fossil fuel units. Comparisons between 1977 and 1978 control and discharge data, however, are suggestive of a reduction in biological impacts within the discharge basin possibly resulting from the March through September 1978 shutdown period for Unit 3. It is anticipated that further comparative data from both control and discharge basins should confirm or negate relationships between Unit 3 operation and biological standing crop, possibly by the conclusion of the 1979 sampling year. O xiii
INTRODUCTION The purpose of this study is to determine the condition of the benthic and zooplanktonic communities in the area directly affected by the thermal plume from the Crystal River power generating plant. The sampling program was designed to yield data that would indicate significant changes which may occur due to the operation of Crystal River Unit 3. The 1977 Final Report was submitted to Florida Power Corporation on 13 July 1978, which presented results obtained during the four quarterly sampling periods of 1977 and comparisons of the 1977 results with those obtained in the pre-operational studies. The following 1978 Final Report includes data from the four quarterly sampling periods of 1978 and compares the complete 1978 results with those obtained in both the pre-op+ rational studies and the 1977 study. Strict comparisons, of course, have been limited to those data for which sampling areas and procedures were essentially the same for p r e -o p e r a t '. o n a l and post-operational studies. Direct compariscns and frequent references are made between the post-operational studies because sampling stations, procedures, and analyses have been identical for both years. O I-l
The study area is shown in Fig. 1. The discharge and control basins are separated by a system of jetties h constructed to restrict the flow of the thermal effluent from mixing with water entering the intake canal. Also shown in Fig. 1 are the samplice stations at six discharge oyster reefs and three control oyster reefs located in the inner basins and the two zooplankton stations located about four kilometers distant from the respective basins. Benthic sampling stations not associated with oyster reefs are shown in Fig. 2. These include seven discharge stations and five control stations. Three discharge and two control inside radials also are shown which are paths along which the condition and percent cover of seagrasses are monitored. The seagrass monitoring transects for the outside areas are shown in Fig. 3. Seagrass monitoring in these outside areas became part of the study in June 1978. O I-2
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MATERIALS AND METHODS O Field Operation Bottom Core Samples To collect the smaller macroinvertebrates, a 10 cm (diameter) x 15 cm (deep) aluminum core sampling device equipped with a top vent is used. The diver opens the vent and works the device into the substrate by twisting the handles. When the handles reach a depth of 15 cm (or solid rock in some i ns tance s) , the vent is closed before retrieval. The resulting suction helps retain the sample and minimize loss. The cap is then secured over the open end of the coring device to prevent sample loss. At the boat the sample is washed through a 0.5 mm sieve. The washed sample is put into a labeled container and preserved in 10% buffered formalin in seawater. Rose Bengal (100 mg/1) is added on shore (Mason and Yevich, 1967). Five replicate samples are taken at each station. Venturi Samples The larger macroinvertebrates are collected using a venturi suction pump consisting of two Gorman Rupp 16 hersepower pumps connected in parallel, each operating at approximately 80 psi. A three-inch intake hose on each 9 I-6
pump is reduced to a 2 1/2 inch (6.4 cm) outlet hose. These non-collapsible hoses are connected to a diver-operated venturi suction no::le with the outlet restricted to four backward-thrusting 3/4 inch (1.9 cm) copper pipes. The nossle is a four-inch diameter PVC pipe and the outlet is a rigid six-inch diameter hose to which is fitted a 1/3 inch (0.3 cm) mesh nylon bag for retaining the sample. A one square meter aluminum box (0.6m deep), used to define the sample area, is randomly placed on the bottom and worked into the substrate. A diver directs the nozzle towards the substrate, which is drawn into the collecting bag. The sample is taken to a depth of 20 cm where possible. Samples are transferred from the collecting bags to 5 gallon plastic buckets and preserved in a 10% buffered formalin in seawater solution, to which Rose Bengal (100 mg/1) is added. One sample is taken at each benthic sampling station shown in Figure 2. Benthic Plant Samples A 0.25 m aluminum box is placed on the bottom by random casts. Divers collect all grasses and macroalgae within the box, including all roots, rhizomes, and holdfasts. Samples are placed in labeled containers and preserved in I-7
10% buffered formalin in seawater. Three replicate samples are taken at each benthic sampling station shown in Figure 2. Sea Grass Monitoring This monitoring program assesses the composition and general condition of macrophytes in the discharge and control areas. Two sets of transects are monitored in each area. The inside radials (two control and three discharge, Fig. 2), located in the general proximity of the benthic sampling stations, are monitored at 0.1 km intervals. The outside transects (six control and 17 discharge, Fig. 3), ranging up to 8 kilometers from shore, are monitored at 0.5 km intervals. Weighted PVC frames, used to delineate 1 m quadrats, are randomly placed on the bottom at each monitoring location. Divers estimate the percent cover, as well as the general growth condition, of seagrasses, the presence of macroalgae (by genus), cnd the presence and abundance of epiphytes within each quadrat. Five replicate quadrats are analyzed at each monitoring location. Oyster Reefs At low tide on the exposed oyster reef, a 9 m rope with a mark at 4.5 m is stretched from the edge of the tidal wash I-8
at one end of the reef to the 9 m point midway between the lateral margins of the exposed reef. An aluminum 0.25 2 ia box is placed at the 4.5 m and 9 m points. The perimeters of the sample quadrats are marked and all macerial within the quadrats to a depth of at least 10 cm is removed, placed into marked gallon jars, and preserved in 10% buffered formalin in seawater. Rose Bengal is added on shore. The two replicates from each reef are randomly selected because their location is determined by the exact position of tidal incursion over the ends of the reef at the time of collection. Zooplankton Samples Zooplankton populations are sampled with a 0.5 m, 202 m mesh net, with a General Oceanics digital flow meter positioned slightly off center across the net mouth. A second flow meter on a separately towed hoop is used for comparisons of the flow meter readings to estimate the percent clogging of the net. The net and the separate meter are towed for two minutes at approximately two knots. Flow meter readings are recorded before and after the tow. The sample is washed down the net into the attached collecting bottle which then is labeled and preserved in 101 buffered formalin in seawater. At each station, two replicate tows are taken at the surface and S I-9
at mid-depth. Zooplankton samples at each station are taken during day and night on two consecutive days for a h total of 16 samples at each station for each sampling period. Environmental Parameters At each station, dissolved oxygen and water temperature were determined using a YSI 57 DO meter. Salinity was measured on a YSI 33 SCT meter. Both meters were calibrated daily in the field. Percent cloud cover was estimated during the collecting of zooplankton samples. O O I-10
Laboratory Operation Quality Control Review The processing of samples from the Crystal River Community Structure Study is assured of quality control by a quality control team organized specifically for this project. Members of this team are among the leading experts in their respective fields in the south Florida area. Their names, affiliations and areas of participation are listed below. Dr. Jeffrey S. Prince Macroalgae University of Miami Mr. Mark P. McMahon Aquatic Vascular Plants Connell Metcalf & Eddy Mr. Edward J. Zillioux Zooplankton Connell Metcalf & Eddy Mr. Lawrence W. Clow Annelids University of Miami Dr. Lowell P. Thomas Crustaceans, Mollusks and University of Miami other Phyla and Mr. Julio Garcia-Gomez Connell Metcalf & Eddy and University of Miami Much time was expended during the initial phases of this work by the quality control team to organize the sorting and identification procedures and to assure the accuracy of the initial identifications. I-ll
Throughout the course of the study each mamber of the team confirmed both species identifications and numbers of individuals from representative samples, and checked the accuracy of all voucher collections within their specific areas of responsibility. Bottom Core Samples Each bottom core sample is washed twice in freshwater
~
through 2 mm and 0.5 mm sieves. This results in " coarse" and " fine" fractions. Each fraction is sorted under the dissecting scope into four general categories of vermiforms, crustaceans, mollusks, and others. These e groups are transferred to a solution of 40% isopropyl alcohol. Polychaetes, mollusks, and crustaceans are identified to species or to family; all other groups ace iden' i f ied to phylum. For biomass determinations, the preserved wet weights for the groups are recorded. The grouped samples are then dried at 70 C for 24 hc rs and reweighed on a Mettler H10 balance to obtain dry weights. Each replicate sample is analyzed separately. Venturi Samples Each venturi sample is washed in freshwater and sieved through a 2 mm mesh. The resulting sample is placed into O I-12
a large glass sorting tray and sorted by hand into the four major groups described above. Any organism less than 0.3 c:a in length is not counted to avoid bias due to differential clogging of the 0.3 cm collecting bag. Identifications and biomass determinations are identical to those described for the bottom core samples. Benthic Plant Samples Benthic plant samples are sorted into seagrass and macroalgae fractions. The seagrasses are identified to species. In each sample fifty leaves (if available) of each species are measured to the nearest millimeter. Mean leaf length and standard error are calculated for each species. Biomass determination is the same as in the first two cases, except that an Ohaus Harvard Trip Balance is used for wet weights of large samples. Biomass is determined by species. Macroalgae are identified to genus. Biomass is determined by the method described above for seagrasses. Macroalgae biomasses are determined for divisions (Rhodophyta, Chlorophyta, Phaeophyta). I-13
Oyster Reefs O Oyster reef samples are sorted in a large glass tray. Crustaceans and mollusks other than oysters are placed into jars of 40% isopropyl alcohol and identified to species. Adult oysters and spat are separated (" adults" are distinguished from " spat" by shell lengths greater than 2 cm), and the numbers of each are recorded. Each adult oyster is opened, the shell length measured to the nearest millimeter, and the meat placed into jars of 40% isopropyl alcohol. Mean oyster shell length and standard error are calculated for each sample. Biomass determinations for oyster meat are made on the triple beam balance, dried for 48 hours at 90 C, and reweighed. The procedures used in biomass determinations for the O crustaceans, spat and other mollusks are identical to those described for bottom cores. Zooplankton Samples Aliquots of the zooplankton samples are prepared by using a modification of the Langford Plankton Sub-sampler as described by C. E. Cushing, Jr. (1961). The aliquot size depends on the amount of phytoplankton and relative density of zooplankton organisms. Taxonomic identifications and counts e.e determined under the O I-14
dissection scope with the use of a channelled slide of 6 al capacity. All unusual sample characteristics are recorded. The number of organisms m' are determined by the following formula: YNC m7-where Y = the inverse of the aliquot size, N = the number of counts, C = the aliquot correction factor, and V = the volume passing through the net, determined by the flow meter readings. Biomass determinations are made by weighing aliquots of the samples, drying at 60 C for 24 hours, and reweighing. These weights are multiplied by the inverse of the aliquot fraction ano the aliquot correction factor to determine the actual biomass of the entire sample. Voucher Collection voucher specimens of all benthic taxa are maintained whenever possible. A photographic voucher collection of zooplankton is being compiled. The quality control team has confirmed the identifications of all voucher taxa. I-15
RESULTS O General Comments The data collected during the quarterly sampling periods of 1978 are s umma r iz ed in Figs. 4 through 57 and Tables 1 through 18. For reference purposes, all raw data and their basic statistics have been coded by taxon and stored in a computer-retrievable system. The results reported here are presented in sections which correspond to the type of sample collected. Animals collected by the venturi suction sampler and the bottom core sampler, however, are reported together in the section on benthic invertebrates as they represent a planned sampling redundancy within the same habitats. Appropriate O statistical analyses of these data are included in the tables presented in Appendix B. A complete list of all benthic and zooplankton taxa is given in Tables 1, 2 and 3 collectively. The relative frequency of occurrence of each benthic or oyster reef taxon (Tables 1 and 2, respectively) is indicated by the percentage of control or discharge stations where it was found. The relative frequency of occurrence of each zooplankton taxon (Table 3) is indicated by the percentage of control or discharge samples in which it was found. O I-16
Table 1. Taxonomic list and relative occurrence of benthic organisms (excluding organisms found only on oyster reef s) , in the vicinity of Florida Power Corporation's Crystal River Plant. (Each relative occurrence datum is the percentage of 20 control stations or 28 discharge stations where occurrence was recorded. A relative occurrence of zero f or both the control and discharge basins indicates species presence in 1977 but not in 1978. Samples were collected during March, June, September and December 1978.) Relative Occurrence Control Discharge Taxon Stations Stations PHYLUM ANNELIDA, CLASS POLYCHAETA Amphicteis gunneri Ampharetidae 5 11 Apoprionospio pygmaea Spionidae 10 4 Arabella iricolor Arabellidae 85 18 Arabella irudescens Arabellidae 0 0 Arenicola cristata Arenicolidae 10 21 Aricidea fragilis Paracnidae 0 0 Aricidea philbinae Paraonidae 90 100 Aricidea taylori Paraonidae 80 100 Aricidea sp. Paraonidae 25 29 Axiothella mucosa Maldanidae 80 43 Branchioasychis americana Maldanidae 65 43 Capitella capitata Capitellidae 70 71 Ceratonereis sp. Nereidae 5 11 Chone duneri Sabellidae 90 54 Chone sp. Sabellidae 0 0 Clymenella torcuata Maldanidae 0 21 Dasybranchus lumbricoides Capitellidae 0 4 Diopatra cupria Onuphidae 20 43 Enoplocranchus sa,nguineus Terecellidce 5 0 Eteone heteropoda Phyllodocidae 50 25 Eumida sanguinea Phyllodocidae 0 4 Eunice pinnata Eunicidae 0 0 Exogone dispar Syllidae 75 11 Exogone sp. Syllidae 0 0 Fabricia sabella Sabellidae 5 0 Fabricia sp. Sabellidae 65 18 Glycera americana Glyceridae 55 52 Glycinde solitaria Goniadidae 0 0 Glycinde sp. Goniadidae 15 0 Gyptis brevipalpa Hesionidae 75 57 Haploscoloplcs robustus Orbiniidae 85 57 Harmothoe aculeata Polynoidae 10 14 Heteromastus filiformis Capitellidae 20 39 Hyboscoi3x longiseta Scalibregidae 10 0 Laeonereis culveri Nereidae 40 82 Lepidametria commer alis Polynoidae 55 0 Lepidonotus sp. Po.!ynoidae 30 7 I-17
Table 1. (Cont.) Relative Occurrence Control Discharge Taxon Stations Stations Loandalla fauveli Pilargidae 0 0 Lumbrineris sp. Lumbrinereidae 40 75 Lysidice ninetta Eunicidae 0 7 Lysilla alba Terebellidae 60 14 Magelona pettiboneae Magelonidae 50 54 Malacoceras vanderhorsti Spionidae 5 4 Marphysa sanguinea Eunicidae 75 79 Mediomastus californiensis Capitellidae 65 82 Melinna maculata Ampharetidae 20 11 Minuspio cirrifera Spionidae 0 0 Minuspio cirrobranchiata Spionidae 5 4 Nainereis sp. Orhiniidae 45 14 Nereis acuminata Nereidae 10 14 Nereis falsa Nereidae 25 25 Nereis succinea Nereidae 50 43 Nereis sp. Nereidae 25 14 Notomastus latericeus Capitellidae 0 7 Onuphis nebulosa Onuphidae 95 39 Oweniidae 14 Owenia fusiformis 5 Paramastis speciosa Capitellidae 0 0 Paranaitis speciosa Phyllodocidae 5 0 Paraonides sp. Paraonidae 65 25 Paraonis sp. Paraonidae 30 21 Paraptionospio pinnata Spionidae 45 61 Pectinaria gouldii Pectinariidae 30 11 Perinereis floridana Nereidae 0 0 Phyllodoce arenae Phyllodocidae 5 7 Phyllodoce sp. Phyllodocidae 0 7 Pilargis sp. Pilargidae 0 0 Piromis eruca Flabelligeridae 5 0 Pista cristata Terebellidae 45 25 Pista palmata Terebellidae 25 14 Pista sp. Terebellidae 5 0 Platynereis dumerilii Nereidae 40 11 Poecilochaetus johnsoni Poecilochaetidae 25 11 Polydora websteri Spionidae 45 50 Polyondontes lupina Polycadontidae 0 7 Prionospy heterobranchia Spionidae 55 43 Sabella micropthalma Sabellidae 45 11 Sabellaria vulgaris Sabellariidae 20 4 Sabellaria sp. Sabellariidae 0 0 Schistomeringus rudolphi Arabellidae 30 0 Scolelepis sauamata Spionidae 30 36 Scoloplos rubra Orbiniidae 80 71 Scychoproctus platycroctus Capitellidae 35 4 I-18
Table 1. (Cont.) Relative Occurrence Control Discharge Taxon Stations Stations Sigambra bassi Pilargidae 5 0 Sphaerosy111s sp. Syllidae 5 0 Spio pettibonae Spionidae 0 4 Spiochaetopterus costarum Chaetopteridae 0 0 Spiophanes bombyx Spionidae 0 14 Streblosoma h,rtmanae Terebellidae 50 4 Streblospio b'enedicti Spionidae 10 29 Syllides sp. Syllidae 0 0 Syllis sp. Syllidae 90 43 Tharyx sp. Cirratulidae 95 71 unid. sp. Arabellidae 0 4 unid. sp. Capitellidae 65 61 unid sp. Cirratulidae 0 0 unid. sp. Dorvillidae 0 0 unid. sp. Hesionidae 0 0 unid. sp. Lumbrinereidae 0 0 unid. sp. Maldanidae 0 4 unid. sp. Nereidae 45 43 unid. sp. Oligochaeta 70 57 unid. sp. Opheliidae 0 4 unid. sp. Orbiniidae 5 4 unid sp. Paraonidae 15 29 unid. sp. Phyllodocidae 20 4 unid sp. Polynoidae 5 0 unid. sp. Sabellidae 30 11 unid. sp. Scalibregnidae 5 0 unid. sp. Serpulidae 35 4 unid. sp. Spicnidae 40 43 unid, sp. Syllidae 35 7 unid. sp. Terebellidae 40 18 unid. Annelida -- 0 4 PHYLUM MOLLUSCA, CLASS GASTROPODA Acteocina c,2,1aliculata Acteocinidae 65 79 Acteccina byllata Acteocinidae 0 4 Acteon punctostriatus Acteocinidae 0 4 Anachis obesa Columbellidae 10 0 Anachis pulchella Columbellidae 0 4 Anachis semiplicata Columbellidae 20 0 Bittium varium Cerithiidae 15 14 Bulla striata Eullidae 25 11 Bulla sp. Bullidae 15 7 I-19
Table 1. (Cont.) Relative Occurrence Control Discharge Taxon Stations Stations Caecum pulchellum Caecidae 0 4 Caecum sp. Caecidae 20 25 Calatrophon ostreatum Muricidae 30 0 Cancellaria reticulata Cancellaridae 15 7 Cerithiopsis emersoni Cerithiidae 5 0 Cerithium eberneum Cerithiidae 13 4 Cerithium_ muscarum Cerithiidae 70 14 Cerithium sp. Cerithiidae 5 4 Crassispira tampaensis Turridae 0 0 Crepidula aculeata Calyptraeidae 15 0 Crepidula maculosa Calyptraeidae 85 7 Crepidula plana Calyptraeidae 45 11 Crepidula sp. Calyptrae idae 7 4 Diadora cayenensis Fissurellidae 15 0 Diadora jaumei Fissure 11idae 0 0 Epitomium sp. Epitoniidae 5 0 Facciolaria lilium Fasciolariidae 0 0 Gemma sp. Leptonidae 0 4 Granula ovuliformis Marginellidae 55 4 Haminoea sp. Haminoeidae 25 32 Marginella apicina Marginellidae 90 0 Marginella aureocincta Marginellidae 10 0 Marginella lavaleeana Marginellidae 15 0 Marginella sp. Marginellidae 5 4 Melanella sp. Melanellidae 5 0 Melongena corona Melongenidae 20 4 Mitrella lunata Columbellidae 35 50 Nassarius vibex Nassaridae 60 54 odostomia sp. Pyramidellidae 35 43 Olivelia mutica Olivellidae 5 0 Olivella sp. Olivellidae 30 4 Polinices duplicatus Natacidae 15 4 Pyramidella sp. Pyramidellidae 0 0 Pyrgocytha.ra plicosa Turridae 0 4 Rissoina sp. Rissoinidae 5 0 Strombiformis sp. Strombidae 0 4 Teinos'a_ma sp. Vi t.r inellidae 20 14 Turbonilla sp. Pyramidellidae 20 14 Urosalpinx tampaensis Muricidae 0 0 unid. sp. Nudibranchia 0 4 unid sp. Turridae 0 0 0 T-20
Table 1. (Con t. ) Relative Occurrence Control Discharge Taxon Stations Stations PHYLLUM MOLLUSCA, CLASS BIVALVIA Abra aequalis Semelidae 10 4 Aligena texasiana Leptonidae 0 4 Amygdalum papyrium Mytilidae 15 43 Arcopsis adamsi Arcidae 5 0 Argopecten irradians Pec tinidae 5 0 Brachidentes domingensis Mytilidae 0 0 Carditamera floridana Carditidae 60 0 Chione cancellata Veneridae 10 18 Chione sp. Veneridae 0 0 Codakie sp. Lucinidae 5 4 Corbula dietziana Corbulidae 0 0 Corbula swiftiana Corbulidae 5 0 Corbula sp. Corbulidae 5 0 Crassostrea virginica Ostreidae 35 11 Cumingia cearetata Semelidae 15 7 Cumingia sp. Semelidae 0 7 Ensis minor Solenidae 5 14 Ischadium recurvum Mytilidae 40 7 Laevicardium mortoni Cardiidae 60 21 Lima pellucida Limidae 5 4 Lieberus castaneus Mytilidae 0 0 Lucina nassula Lucinidae 0 0 Lyonsia hyalina Lyonsiidae 55 43 Mercenaria campechiensis Veneridae 0 11 Musculus lateralis Mytilidae 30 'l Mysella planulata Leptonidae 40 39 Mysella sp. Leptonidae 0 0 Nucula crenulata Nuculidae 5 0 Nuculana sp. Nuculidae 0 4 Ostrea equesris Ostreidae 25 7 Parastarte triquetra Veneridae 0 4 Pe_riploma sp. Periplomatidae 0 0 Pleuremeris tridentata Carditidae 0 0 Semele porficua Semelidae 20 11 Semele sp. Semelidae 0 0 Solemya sp. Solemyacidae 0 0 Tagelus divisus Solecurtidae 0 11 Tellina lineata Tellinidae 5 0 Tellina texana Tellinidae 5 4 Tellina sp. Tellinidae 40 54 Transenella copradina Venertuae 35 11 unid, sp. Carditidae 5 0 I-21
Table 1. (Con t. ) Relative Occurrence Control Discharge Taxon Stations Stations unid. sp. Leptonidae 0 4 unid, sp. Semelidae 0 4 unid. Bivalvia - 0 0 PHYLUM MOLLUSCA, CLASS AMPHINEURA Ishnochiton papillosus Ischnochitonidae 45 0 Acanthochitona pyamaea Acanthochironidae 30 7 PHYLUM ARTHROPODA, CLASS CRUSTACEA Subclass Ostracoda unid. ep. 60 54 Subclass Copepoda unid. sp. 0 4 Order Calanoida unid. sp. 25 21 Subclass Malacostraca Order Cumacea unid sp. Diastylidae 35 21 unid. sp. non-Diastylidae 20 25 unid. Cumacea -
! 4 Order Tanaidacea Kalliapeeudes sp. Kalliapseudidae 20 4 unid. sp. Kalliapseudidae 0 0 unid. sp. Monokonophora 30 4 unid. sp. Dikonophora 45 25 Order Isopoda unid. sp. Aegidae 0 0 unid. sp. Anthuridae 35 29 unid, sp. Cirolanidae 20 0 I-22
Tcble 1. (Con t. ) Relative Occurrence Control Discharge Taxon Stations Stations unid. sp. Excorallinidae 0 0 unid, sp. Idoteidae 45 46 unid sp. Sphaeromatidae 35 4 unid. Isopoda -- 10 0 Order Amphipoda unid. sp. Ampeliscidae 80 54 unid, sp. Amphilochidae 45 4 unid. sp. Ampithoidae 75 61 unid. sp. Aoridae 75 71 unid. sp. Bateidae 30 4 unid. sp. Caprellidae 20 0 unid. sp. Colemastigidae 5 0 unid. sp. Corcphiidae 45 18 unid sp. Gammaridae 0 0 unid. sp. Hyalidae 0 0 unid. sp. Leucothoidae 10 0 unid. sp. Liljeborgiidae 45 7 unid. sp. Lysianessidae 15 0 unid. sp. Melitidae 55 29 unid, sp. Mysidacea 5 0 unid sp. Phliantidae 15 0 unid. sp. Phoxocephalidae 25 0 unid. sp. Puntogeneidae 20 0 unid sp. Stenothoidae 10 0 unid. sp. -- 15 4 Order Decap.da Alpheus armillatus Alpheidae 25 0 Alpheus heterochaelis Alpheidae 60 25 Alpheus normannii Alpheidae 30 18 Alpheus sp. Alpheidae 30 18 Ambidexter symmetricus Hippolytid.ie 50 46 Callinectes sapidus Portunidae 0 0 Callinectes sp. Portunidae 0 4 Eurypanopeus abbrr:viatus Xanthidae 0 0 Eurypanopeus depressus Xanthidae 40 7 Eurypanopeus dissimi).s Xanthidae 10 0 Eurypanopeus sp. Xanthidae 0 7 Hexapa4opeus aucustifrons Xanthidae 0 0 Hippolvte pleuracantha Hippolytidae 70 39 Hippolyte zostericola Hippolytidae 5 0 Hippolvte sp. Hippolytidae 15 0 I-23
Table 1. (Con t. ) Relative Occurrence C"ntrol Discharge Stations Stations Taxon Majidae 20 0 Libinia dubia Majidae 0 0 Libinia sp. Majidae 0 0 Metophorhaphis sp. Xanthidae 35 4 Neopanope packardi Neooanope texana Xanthidae 60 25 Xanthidae 95 29 Neopanope sp. Ogyridae 0 0 Ogyrides limicola Ogyridae 10 0 Oqyrija3 yaquiensis Ogyridiae 0 0 ogyrides sp. Palaemonidae 25 0 Palaemon floridanus Palaemonidae 0 0 Palaemon sp. Palaemonetes intermedius Palaemonidae 40 21 Dalaemonidae 10 7 Palaemonetes pucio Palaemonetes sp. Palaemonidae 5 7 Pagurus annulipes Paguridae 0 0 Paguruc spp. Pt.guridae 100 36 Panacopsis sp. Panae idae 0 0 Panopeus herbstii Xanthidae 20 0 Panopeus occidentalis Xanthidae 10 4 Panopeus sp. Xanthidae 0 4 Majidae 5 0 Pelia mutica Penaeus sp. Panaeidae 35 43 Periclimenes americanug Palaemonidae 25 14 Periclimenes lonoicauf.atus Palaemonidae 30 25 Periclimenes sp. Palaemonidae 5 4 Petrolisthes armat3s Porcellanidae 10 4 Pinnixa sp. Pinnotheridae 35 29 Rithropanopeus harrisii Xanthidae 25 25 Hippolytidae 20 21 Thor _ floridanus Tezeuma carolinense Hippolytidae 15 14 upogebia affinis Callianassidae 45 21 unid. sp. Alpheidae 0 0 unid. sp. Callianassidae 10 4 unid, sp. Majidae 5 0 unid, sp. Paguridae 10 0 Palaemonidae 20 4 unid. sp. unid, sp. Penaeidae 5 7 unid. sp. Pinnotheridae 10 4 unid. sp. Xanthidae 55 29 unid. sp. sect. caridean 7 10 unid. sp. Brachyuran zoea 5 7 Caridean zoea 10 7 unid. sp. unid. Natar.tia - O 11 I-24
Table 1. (Cont. ) Relative Cccurrence Con tr ol Discharge Stat nns Stations Taxon Subclass Cirripedia Balanidae 25 11 Balanus sp. Subclass Cephalocardia 5 0 unid, sp. Order Cyclopoida 5 4 unid, sp. 8C 64 PHYLLE ECHINODERMATA 80 29 PHYLLH ASCHELMINTHES 60 18 _ _:'" 'N S I PUN CULA 100 71 PHYLLH NEMERTINEA 25 18 PHYLLH PLATYHEI24INTHES PHYLLH CHORDATA TC 7 CLASS ASCIDIACEA E 61 CLASS OSTEICHTHYES PHYLLH PORIFERA 4L 4 0 7 PHYL124 CHAEIOGNATHA 5 0 PHYLLH COELENTERATA 5 0 PHYLLH ECTOPROCTA MACROALGAE DIVISION RHODOPHYTA Ceramiaceae 3 0 Ceranium sp. Champiaceae 15 0 Champia sp. Rhodoymeniaceae 0 0 Chrysymenia sp. Rhodomelaceae 40 0 Chondria sp. 25 0 pasya sp. Dasyaceae I-25
Table 1. (Cont ) R"lative Occurrence Control Discharge Taxon Stations Stations Digenia sp. Rhodomelaceae 5 0 Gracilaria sp. Gracilariaceae 40 7 Hypneaceae 0 0 Hyonea sp. Laurencia sp. Rhodomelaceae 10 0 Polysiphonia sp. Rhodomelaceae 0 4 Ceramiaceae 25 0 Sy ridia sp. DIVISION PHAEOPHYTA Dictyota sp. Dictyotaceae 10 0 Sargassum sp. Sargassaceae 55 0 Stictyosiphon sp. Striariaceae 15 7 Stilophora sp. Stilophoraceae 15 0 DIVISION CHLOROPHYTA Acetabularia sp. Dascyladaceae 0 0 Caulerpa sp. Caulerpaceae 50 0 Cladophora sp. Cladophoraceae 0 4 Halimeda sp. Codiaceae 0 0 Penicillus sp. Codiaceae 0 0 Udotea sp. Codiaceae 15 0 SEAGRASSES Halodule beaudettei Cymodoceaceae 15 95 Halophila engelmannii Hydrocharitcceae 25 0 Ruppia maritima Ruppiaceae 40 0 Syringodium filiforme Cymodoceaceae 20 0 Thalassia testudinum Hydrocharitaceae 5 0 0 I-26
Table 2. Taxonomic list and rels .ve occurrence of benthic organisms on oyster reefs in the vicinity of Florida Power Corporation's Crystal River Plant. (Each relative occurrence datum is the percentage of 12 control or 24 discharge stations where ,ccurrence was recorded. Samples were collected during March, June, September and December 1978.)
~~~
Relative Occurrence Control Discharge Taxon Stations Stations PHYLUM MOLLUSCA, C' ASS GASTROPOD A Crepidula plana Ca'.;7 tr a e idae 59 0 Fasciolara lilium Fasciolariidae 8 0 Crepidula maculosa Calyptraeidae 8 0 17 0 Cerithium muscarum Cerithiidae Cerithiopsis emersoni Cerithiidae 8 0 Odostomia sp. Pyramidellidae 0 8 PHYLUM MOLLUSCA, CIASS BIVALVL. Carditamera floridana Ca r .J.tidae 42 0 Corbula sp. Corbu_idae 8 0 Crassostrea virginica Ostre dae
. 100 100 Ischadium recurvum Mytil.Jae 93 79 Ostrea equestris Ostre.dae 42 0 Semele porficua Semel.dae 42 0 PHYLUM MOLLUSCA, CIASS AMPHINEURA Acanthochitona pygmaea Ac.athochitonidae 22 0 Ischnochiton papillosus Ischnochitonidae 11 0 PHYLUM ARTHROPODA, CLASS CRUST?CEA Subclass Malacostraca Order Tanaidacea unid. sp. Dikonophora 0 0 Order Amphipoda unid. sp. nya?.idae 68 45 unid, sp. Melitidae 11 0 unid. Amphipoda -- 0 11 Order Decapoda Eurypancpeus depressus Xanthidae 85 95 Eurypanopeus sp. A nthidae 0 0
-27
Table 2. (Continued) Relative Occurrence Control Discharge Taxon Stations Stations Neopanope packardi Xanthidae 11 0 Panopeus herbstii Xanthidae 93 75 Panopeus occidentalis Xanthidae 25 4 Petrollsthes armatus Porcellanidae 51 8 Rithropanopeus harrisii Xanthidae 11 0 Uca pugilator Ocypodidae 0 11 Uca sp. Ocypodidae 11 4 unid. sp. Grapsidae 0 11 unid sp. Xanthidae 85 87 Subclass Cirripedia Balanus sp. Balanidae 76 75 Phylum Insecta Anurida maritima ~-duridae 25 4 unid. arachni.d -- 11 0 0 e I-28 i
Table 3. Ta.<onomic list and relative occurrence of ::coplankton in the vicinity of Florida Power Corporation's Crystal River Plant. (Emch relative o currence datum is the percentage of 32 discharge or 31 control samples where occurrence was recorded. Samples were collected during Jun and December 1978.) Relative Occurrence Control Discharge Samples Samples Taxon PHYLUM 03FL"iTERATA r CLASS HYDROZOA 52 41 unid. Anthomedusae unid. Leptomedusae 42 31 3 0 ScypLacan medusae PHYLUM PLATYH204INTHES 10 0 unid. spp. PHYLUM ANNE.IDA CLASS POLYCRAETA t 0 unid. sp. unid. larvae 17 81 PHYLUM ECTOPR".CTA unid. cynhonautes larvae 39 72 PHYLUM CHAEIOGNATHA Sacittu sp. 100 04 PH'fLUM 93LLUSCA CLASS Gi/1 PODA 100 100 unid. ve!_gers 1-29
Table 3. (Cont. ) Relative Occurrence Control Discharge Samples Samples Taxon CLASS BIVALVIA unid, veligers 100 100 unid. species, juvenile 3 0 PHYLUM ECHINODERMATA CLASS OPHIUROIDEA unid. ophiopluteus 16 38 unid. echinopluteus 3 3 PHYLUM ASCHELMINTHES CLASS NEMATODA unid. spp. 0 0 PIIYLUM CHORDATA CLASS OSTEICHTHYES unid. eggs 90 56 unid. larvae 29 47 unid. juveniles 0 0 SUBPHYLUM TUNICATA unid. Larvacea 97 100 0 I-30
Table 3, (Cent. ) Relative Occurrence Control Discharge Taxon Samples S amples PHYLL?i ARTHROPODA, CLASS CRUSTACEA unid. sp. 23 13 Subclass Copepoda unid, nauplii 29 31 Order Calanoida unid. nauplii 13 31 unid. sp. 23 13 Acartia tonsa 100 100 Centropages ef. hamatus 23 9 Labidocera mirabilis 90 50 Labidocera scotti 48 28 Labidocera sp. 26 38 Paracala y crassirostris 100 100 Paracalanus parvus 94 88 Pseucodiaptomus coronatus 90 94 Temora turbinata 58 50 Tortanus setacaudatus 0 3 Order Cyclopoida Corycaeus spp. 19 16 Oithona spp. 100 100 unid spp. 58 28 Order Harpacticoida Euterpina acutifrons 97 100 Metis sp. 19 3 - Microsetella sp. 0 0 Porcellidig sp. 0 0 unid. spp. 16 47 Tegastidae 39 28 sp. A. 71 47 Order Monstrilloida unid. sp. 0 0 I-31
- 'able 3. (Con t. )
Relative Occurrence Control Discharge Samples Samples Taxon Subclass Cirripedia unid. nauplii 100 100 42 47 unid cypris Subn ass Ostracoda 10 3 unid, spp Subclass Branchiopoda Order Cladocera unid. sp. 10 13 S :bclass Malacostraca 2rder Amphipoda O unid spp. 26 22 Order Mysidacea 6 3 unid, spp. Order Cumacea 23 3 unid. spp. Order Isopoda unid. spp. 100 88 Order Tanaidacea 0 0 unid. sp.
.cder Decapoda 6 0 unid. larvae O
I-32
Table 3. (Con t. ) Relative Occurrence Control Discharge Sarnoles Samples Taxon Suborder Natantia 94 94 caridean zoea 0 0 m, sis larvae 39 22 post larvae 19 6 Lucifer sp. 0 0 Pericli:tenes sp. Suborder Reptantia 13 6 porcellanid zoea 52 56 brachyuran zoea 6 3 megalopa 3 0 Paguridae (Anomura) PHYLUM ARTHROPODA, CLASS ARACHNIDA Order Acarina 10 0 unid. sp. PHYLUM ARTHROPODA, CLASS PYC'K)GCNIDA 0 3 unid. sp. I-33
Over the vcar, these percentages are based upon 48 benthic stations (20 control; 28 discharge), 36 oyster lh reef statier. (12 control; 24 discharge) and 63
- ooplankton :a mple s (31 control; 32 discharge).
The mean temperature and salinity values for control and discharge areas during each sampling period are presented in rigs. 4 and 5, respectively. Both temperature and salinity means always were higher in the discharge area than in the control area and, as expected, there is seasonal variation in both parameters. O O I-33
Fig. 4. Temperature with LT indicated at inside stations of control and discharge basins for different sampling periods of 1978. (Given are means (connected circles) , standard deviations (rectangles) , ranges (horizontal bars) , and number of measurements.) I-35
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Benthic Animals General Treatment Data on overall mean number of individuals, biomass, and species diversity are gi"en below under the separate sub-section heading of Total Animal Benthos. Where appropriate, comparable data on major taxonomic divisions also are presented, causing this section to overlap with the following sections on Polychaetes, Crustaceans, Mollusks and Other Groups. Statistical treatments comparing control and discharge means and testing the effects of temperature, salinity and macrophyte biomass on cbundance, biomass and diversity are reported in these sections for all 1978 data. Additional treatment of benthic animals and other major groups is given in the sections entitled " Grouped Data Summations" and " Comparisons with Pre-operational Data." Based upon the analyses of sample data on the separate taxonomic groups during both 1977 and 1978 post-operational studies, some assumptions are made which contribute to the general treatment of the overall year's data. I-39
The two methods of sampling benthic animals showed large differences in calculated mean numbers p e :. square meter. The bottom core sampler generally sampled the O smaller animals more efficiently while the venturi suction sampler captured the larger animals more efficiently. The major advantage of the venturi suction sampler is its ability to sample an entire square meter rapidly with reasonable thoroughness. Smaller soft-bodied animals are easily damaged, however, and many whole animals, as well as fragments, are lost through the relatively large 0.3 cm mesh of the collecting bag. The five replicates taken at each station with the bottom core sampler encompass a total sampling area of only 0.04 m . This appears adequate for sampling populations of small animals having a high frequency of occurrenca but is inefficient for h larger, less frequent animals. Generally this results in calculation of artificially low numbers of large animals per square meter. Occasionally, however, a chance capture of a large animal such as a starfish can produce artifically elevated numbers thus resulting in highly erratic data. In the following sections, therefore, differences between techniques are taken into consideration i ri data analysis and data from core and venturi samples are always identified and listed separately; with the exception of the treatment of total number of taxa given in Fig. 6. I-40 9
Fig. 6. Total number of species of polychaetes (6A), crustaceans (6B), and mollusks (6C) at discharge and control stations for different sampling periods of 1978. (Numbers in parentheses over bar graphs indicate the percentage of discharge or control stations where at least half of the indicated nunber of species were found) . O I-41
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z / .? . / :- A c MAR 78 JUN 78 SEP 78 DEC 78 O I-42
Total Animal Benthos Within the discharge basin, a mud or mud-sand ooze predominates at all stations. Stations in the control basin are characterized by a mixture of shell, rock, and sand with only occasional mud. With regard to bottom sediment types, therefore, while there is considerable difference between the two basins, station differences within the separate basins are relatively small. Depth of sediments, however, varies irregularly with position. Occurrence and abundance of bottom vegetation are often related to sediment depth and there are demonstrable differences in macrophyte biomass between the various stations within the separate basins. If differences in benthic invertebrate populations between either the control stations or the discharge stations are related to differences in macrophyte biomass, then regressions of the various aopulation parameters on macrophyte biomass should
~
be significant. Total abundance m' , biomass m and diversity from venturi and bottom core samples for both control and discharge basins were tested for dependence on
-2 total mac rophy te biomass m at each station for the respective basins. Significant negative correlations between animal diversity and macrophyte biomass were found for the control venturi samples (r = .33, slope =
I-43
-0.003, . 0 2 < P< . 0 5 ) and for the discharge core samples (r = .17, slope = -0.002, .005<P<.01). This regression was not significant for either control core samples or discharge venturi samples, but observations indicate that certain species tend to predominate in macrophyte associations, thereby accounting for the reduced diversity. The greater macrophyte biomass in the control basin (see section on Seagrass and Macroalgae) probably accounts for the stronger negative regression for the control samples when compared with that for the discharge samples. None of the discharge or control regressions of abundance or biomass on macrophyte biomass was significant. In accordance with rationales given in the 1977 Final Report (p. I-47), normal distribution and equal variance O for either basin are assumed and sample data have been pooled, therefore, for comparisons between control and discharge basins (see section entitled Grouped Data Summa tion s) . The means, standard deviations and ranges of animal abundance sampled by the venturi suction method are shown in Fig. 7 for the control and discharge basins for the four sampling periods in 1978. The means of the control samples were always higher than the means of the discharge samples, particularly in the March, June, and September G I-44
o-------- o CONTROL o e DISCHARGE I400- - l000-
'~~ '
N ,~~~,'s, ' 8 N 2 __ .
"M>
g J o
< /
a .- Q m-O Z
- g T
w g x s E / O z Z W * - . . y to-2- MAR 78 JUN 78 SEP 78 DEC 78 Fig. 7. Mean abundance m'2 of animals col 1ected in venturi sampies in the control and discharge basins during 1979 sampling periods. (Given are means (connected circles) , standard deviations (rectangles) and ranges (horizontal bars) .) I-45
samples. However, in December, the control means were only slightly higher than the discharge means. The same approximate patterns are reflected in the abundance graphs of the major component groups of annelids, mollusks and crustaceans (Fig. 8). Biomass data for the same groups are given for control and discharge basins in Figs. 9 and 10, respectively. Comparable data from the bottom core samples are presented in Figs. 11 through 13. The means, standard deviations and ranges of total animal abundance for control and discharge basins are given in Fig. 11. As expected, the same data for tctal annelids, given in Fig. 12, are very similar. The closeness of this similarity between total animal and annelid abundance is a reflection of the conclusion arrised at during the 1977 study, that larger animals are ir. efficiently captured by the small core samples and annelids alone account for the majority of the animal abundance in these samples. Data for mean annelid bicmass are presented in Fig. 13. The mean abundance for bottom cores is similar for both discharge and control basins during March, June and December, with the control basin having slightly higher means during these periods. In September, the discharge mean is slightly higher (Fig. 11). In contrast, mean I-46
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8 % 15 0 - f' , Os,N'N,N\ s
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<t 50 - ~3 ANNELIDS MOLLUSKS CONTROL @ ----- CRUSTACE ANS BASIN 5
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<C W
2 100 - P
/
/
/
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/ /
./
~~~"
, - +
A .o.________._ I I l i MAR 78 JUN 78 SEP 78 DEC 78 Fig. 8. Mean abundance n~I of annelids, mollusks, and crustaceans collected in venturi samples in the discharge (Bis) and control (83) hasir.s during 1978 sampling periods. I-47
O CONTROL BASIN ANNELIDS MOLLUSKS CRUSTACEANS N I 2 40 m h I T \ / O 30- 'g e -
/ \
\ / \ O co \-
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en
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- O I I I i MAR 78 JUN 78 SEP 78 DEC 78 Fig. 9. Mean biomass m' of annelids, mollusks, and crustaceans collected in venturi samples in the control basin during 1978 sampling periods.
I-48
20.8962
- DISCHARGE
\. BASIN
[ ANNELIDS
- MOLLUSKS 9
/
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i O- i SEP 78 DEC 78 $ Fig. 10. MAR 78 JUN 78 Mean biomass m-2 of an.slids, mollusks, and cruscaceans collected in venturi samples in the discharge I asin during 1978 sampling periods. I-49
raiF arni ne g 2WqZ ZDECW D _ Z O 2 O D < d )(r 2iN 1 g t . emh 1 0 see1 a 1 ,I ,0 ,0 ( nd. 0 0 0 hsi o s 10 0 0 0 r( cM 0 0 0- 0-i che zoaa onrn nng t eea ac b l ennt au M % bddd A a a R N rccn s sioc 7
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2 J SEP 78 DEC 78 g Fig. 12. MAR 78 JUN 78 Mean annelid abundance m"E collected in bottom core samples in the control and discharge basins during 1978 sampling periods. (Given are means (connected circles) , standard deviations (rectangles) and ranges (hori:ontal bars) . ) _
15-O o- ------o CO NT R O L
- : DISCHARGE Ts m
h 5 [ O g 10-v U) y) -- E o 5 - e O _I - W 4 Z 5- - s __ Z \
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MAR 78 JUN 78 SEP 78 DEC 78 Fi g . 13. Mean annelid biomass m"I collected in bottom core samples in the control and discharge basins during 1978 sampling periods. (Given are means (connected circles) , standard deviations (rectangles) and ranges (horizontal bars) .) 5-53
abundance for venturi control samples is much higher for March, June, and September (Fig. 7). However, the small difference found in venturi abundance for December is comparable to that found in the bottom cores for the same period (Fig. 11). The basic statistics for each taxon present in bottom core samples and venturi suction samples are given in Tables B-1 and B-2 of Appendix 2, respectively. Included
~
are the number of individuals m with station means, standard deviations and ranges by taxon, basin and sampling period, and the mean wet and dry weights of each major group for each basin and sampling period. Species diversity and evenness have been calculated for each station both quarterly and annually and are given in Table B-3. The spectra of diversities for venturi and bottom core samples have been graphed against the four sampling periods in Figs. 14A and 14B respectively, for the control and discharge basins. From these data it is apparent that the Shannon-Wiener species diversity index is greater in the control basin when compared to the discharge basin for all sampling periods regardless of the sampling technique. The evenness spectra, graphed in Fig. 15 show somewhat different results. Although evenness is greater in the control basin than in the discharge basin 9 throughout the year for the bottom core samples, evenness I-53
O Fig. 14. Species diversity spectra of benthic animals from venturi samples (14A) and bottom core samples (14B) during 1978 sampling periods. (Given are means (conn ected circles) , standard deviations (rectangles) and ranges (horizon tal bars) . For each control spectrum, n = 5, for each discharge spectrum, n = 7.) I-54
o------o CONTROL
- : DISCHARGE 4-
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~
~
3-I . v 2-p l_ m O' g_ W BOTTOM CORES y 5 B o-----o CONTROL (n : ; DISCHARGE W (_) 4-W Q. _. m
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ty
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2 I VENTURI SAMPLES A MAR 78 JUN 78 SEP 78 DEC 78
.I-55
O Fig. 15. Evenness spectra of benthic animals from venturi samples (15A) and bottom core samples (153) during 1978 sampling periods. (Given are means (connected circles), standard deviations (rectangles) and ranges (horizontal bars) . For each control spectrum, n = 5, for each discharge spectrum, n = 7.) O I-56
o------o CONTROL
- : DISCHARGE I .0 -
0.8-
-~1 $
m J - , 0.6 - . .
^ 0.4 -
e v O.2-ln in BOTTO M CORES W Z B Z y o-----o CONTROL @- y : : DISCHARGE W l .0- ~ G p ~ ' O.8- _ p _______----- -[ _ .
. ______7 0.6-0.4 -
0.2 - VENTURI SAMPLES A JUN 78 SEP 78 DEC 78 g MAR 78 I-57
is greater in the discharge bcsin, throughout the year, for tile venturi samples (see further discussion in section on Grouped Data Summations). In Table 4 benthic abundance, biomass, and diversity for bcttom core and venturi samples are regressed against temperature and salinity. No significant regressions were found for the venturi samples; however, for bottom core samples, dependence was demcastrated for both control and discharge abundance on temperature and salinity, for uischarge biomass on temperature, and for discharge diversity on salinity. Due to these significant regressions run on the overall bottom core data, an additional set of regressions were performed on bottom core data by phyla, in an attempt to partition out those O groups most strongly affected by changes in the chemical and physical regimes in the two basins. Among the well represented phyla, only the annelids showed significant regressions. These will be discussed in the following section on polychaetes. Correlations between temperature and salinity data for the control an.r discharge basins showed a significant positive relationship between the two parameters (control: r = 0. 6 0 9, P <. 0 0 3 and discharge: r = 0. 7 5 6, P < . 0 01) , making it difficult to separate the effects of temperature and salinity on biological data. f I-58
Table 4A. Results of regression analysis of benthic population parameters on physical parameters for the control and discharge basins. Data are f rom the venturi samples of different sampling periods of 1978. (in = 0.05). Dependent Variable Independent Variable d.f. slope r2 Ho: 8=0 Control abundance Temperature 1,18 NA 0.00 do not reject; P>>.25 Discharge abundance Temperature 1,26 NA 0.00 do not reject; .10< P< . 2 5 Control biomass Temperature 1,18 1% 0.04 do not reject; P >. 2 5 g Discharge biomass Temperature 1,26 NA 0.12 do not reject; . 0 5< P <.10 I $ Control diversity Temperature 1,18 NA 0.02 do not reject; P >. 2 5 Discharge diversity Ten.perature 1,26 NA 0.03 do not reject; P >. 25 Control abundance Salinity 1,18 NA 0.01 do not reject; P >.25 Discharge abundance Salinity 1,26 NA 0.01 do not reject; P >.25 Control biomass Salinity 1,18 NA 0.01 do not reject; P>.25 Discharge biomass Salinity 1,26 AA 0.14 do not reject; . 0 5< P <.10 Control diversity Salinity 1,18 NA 0.00 do not reject; P>>.25 Discharge diversity Salinity 1,26 NA 0.02 do not reject; .10<P<.25
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.rt t ae b e d e ae b e d e B en n g g g g g g 4 t e e l r l r l r l r l r l r er d oa oa oa oa oa oa eme n rh rh rh rh rh rh l af e t c t c t c t c t c t c b rf p ns ns ns ns ns ns aai e oi oi oi oi oi oi Tpd D CD CD CD CD CD CD 9
H1c)
Polychaetes The class Polychaeta, collected in the venturi and core samples of March, June, September, and Decemoer 1978. is represented by 35 taxa (see Table 1) . This represents no change in the total number of polychaeta taxa found in 1977 (1977 Final Report: p. I-33). It should be noted, however, that 18 of the taxa found in 1978 were not found in 1977, and, conversely, 18 of the taxa found in 1977 were not found in 1978. In further coincidence, a total of 82 polychaete taxa was found in . ,h basin over the year, with thirteen taxa unique to each area. The seasonal occurrence of these taxa in control and discharge samples is shown in Fig. 6A. As this graph pools all taxa occurrences in 42 discharge samples and 30 control sanples for each sampling period, it is a good indication of the relative abundance of polychaete taxa over the total areas encompassed by the discharge and control stations. Also shown are the relative J ' t ., .atages of discharge and control statior.s where at least if of the indicated total numbers of species were found (this is included as an indication of homogeneity or relative diversity of certain phyla to supplement the Shannon-Wiener and evenness statistics given below in Table 12, Fig. 17, and Fig. 18 on the total benthic 9 population). I-61
Polychaetes found in the discharge basin show a seasonal variation ia number of taxa found of slightly greater than 30% (Fig. 6A). Although the March and September samples were most divergent in total number of taxa, they were most similar in apparent homogeneity. The June and December discharge data seem to represent a transition between the large number of taxa found in March, and the small number of taxa found in September. This trend of a decrease in the number of polychaete taxa from March through September, followed by an increase in December, is reinforced by biomass data for both core and venturi samples (Figs. 10, 13), and by venturi abundance data (Fig. 8A). The bottom core abundance data also reflects this trend (Fig. 11), except for a sharp drop in June to below the September level. The general patterns seen in the 1978 discharge data were also observed in 1977 (1977 Final Report: Figs. 10A, 12, 15, 16). There is a very small difference in number of taxa collected in the control basin between the March, June, and December samples, and a 25% drop in the number of taxa in September (Fig. 6A). September also has the lowest apparent homogeneity among samples, followed by December, with March and June showing a high degree of basin O I-62
homogeneity. The same trend of a decrease in polychaete diversity, abundance, and biomass through September, followed by an increase through December as seen in the discharge basin, is seen in the control bottom ccre data for abundance (Fig. 12), and biomass (Fig. 13) as well as the 1977 control venturi data (1977 Final Report: Figs. 10B, 11). The 1978 venturi samples for abundance (Fig.
- 88) and biomass (Fig. 9), and the 1977 bottom core samples (1977 Final Report: Figs. 15, 16) do not reflect this trend.
A precipitous drop in core annelid abundance and biomass was observed in the control basin for the second, third, and fourth quarters of 1978 (Figs. 12, 13) compared with the same quarters in 1977 (1977 Final Report: Figs, 15, 16). There is less variation in the number of polychaete taxa represented (Fig. 6A), and considerably greater variation in polychaete abundance (Figs. 8, 12) in the control basin than in the discharge basin. Polychaete biomass in the two basins has similar levels of variation over tbc year (Figs. 9, 10, 13). Greater polychaete abundance (Fig. 8) and biomass (Figs. 9, 10) are found in venturi control samples than in venturi discharge samples. However, in the core samples there is no strong I-63
separation of either abundance (Fig. 12) or b i or. a s s (Fig.
- 13) between the two basins. For the last two quarters of the year, fewer polychaetes were found in core control samples than core discharge samples (Fig. 12), although the core polychaete biomass .s slightly greater in the control samples than the discharge samples (Fig. 13) in all sampling periods. No statistical difference between basins could be shown for the bottom core annelid data (Table 13) in 1978. In 1977, however, both abundance and biomass were found to differ in the control and discharge stations for all but the first quarter (1977 Final Report:
Table 12). Annelid abundance and biomass data from bottom core samples were regressed on temperature (Fig. 16) and salinity (Fig. 17) to determine if annelid distribution patterns in the basins are significantly affected by seasonal changes in physical parameters. All of the regressions were negative and significant, demonstrating an inverse relationship between annelid presence, and both temperature and salinity. The regression elevations of control and discharge data were not tested but are obviously similar and, in one case, coincide (Figs. 16, 17). The slopes of the corresponding control and discharge regressions were compared with the Student's t test and were found not o differ significantly (see Figs, 16 and 17 for probability data).
!-64
Fig. 16. Regressions of annelid bicmass (16A) and abundance (16B) on temperature for control and discharge basins. Data are unconverted station totals for bottom core samples of different sampling periods in 1978. (Given are the regression equations, t..e coefficient of determination (r2 ) for the regression, the probability of Ho: S = 0 being true for each regression, the result of comparing the control and discharge slopes, the regression lines and data points. Probability testing at a = 0.05.) 9 I-65
BIOMASS ( G / STATION) ABUNDANCE (No./ STATION)
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Fig. 17. Regressions of annelid biomas', (17A) and abundance (173) on temperature for control and discharge basins. Data are unconverted staticns totals for bc ttom core ss mples of different sampling periods in 1978. (Given are2 th ? regression equations, the coe!!icient of determination (r ) fc r t.se regression, the probability of i!, : 6 = 0 being true for each regression, the result of comparing the control and discharge slopes, the regression lines a d data points. Probability testing at 1 = 0.05.) 9 I-67
BIOMASS ( G / STATION) ABUNDANCE (No./ STATION) m a e m m u u o 8 8 8 8'
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Crustaceans The benthic samples of 1978 contained a total of 87 crustacean taxa, which included 50 taxa of decapods (see Table 1) . Seventy-seven taxa were collected in the control basin and 59 were collected in the discharge basin. Fig. 6B shows a steady decline in the total number of crustacean taxa at the control stations from 61 taxa in March to 32 in December, while the discharge stations show a steady increase from 24 taxa in March to 47 taxa in December. The total number of taxa collected in the discharge basin exceeds the total number collected in the control basin only during the December sampling period. The control stations, however, show a greater apparent homogeneity of taxa when compared with the discharge stations for all sampling periods. The total number of taxa found in the control basin was greater in March 1978 than in April 1977 (Fig. 6B; 1977 Final Report: Fig. SB) . However, for June, September, and December the total number of taxa was greater in 1977 than 1978. Conversely, the number of taxa for discharge samples was greater in April 1977 than in March 1978 and greater in 1978 than in 1977 for corresponding sampling periods throughout the remainder of the year.
~
Mean abundance m for crustaceans collected using fh the venturi suction method increased slightly in the control basin from March to June and then decreased I-69
sharply in September and December. Discharge t aundance increased throughout 'he year with a large it;rease h occurring in December. Control abundance wc; higher than discharge abundance for March, June, and September, but abundance was higher for the discharge basin in December (Fig. 8).
~
Mean biomass m for crustaceans in ventumi samples shows the same general trend as crustacean abundance with biomass being higher in March, June, and September for the control basin and higher in December for the discharge basin (Figs. 9, 10). Comparing Figs. 8, 9 and 10 with the 1977 d its on crustaceans (1977 Final Report: Figs. 10, 11, 1") shows little agreement between the two years in either abundance or biomass. Of particular importance, the e.arp decline in crustacean abundance in the m e u m 01 basin over September and December 1978 compares with a sharp increase over the same period in 1977. In addition, he sharp increase in both abundance and biomass in Decem uer discharge samples for 1978 did rio t occur duri.,7 December 1977. O I-70
Mollusks A total of 80 molluscan species including 44 gastropods, 34 bivalves and two amphineurids were collected during 1978 (Table 1) . Sixty-four species of mollusks were found in the control basin and 58 were collected in the discharge basin. The total number of species decreased over the first three sampling periods in the discharge basin, then increased slightly in December but the magnitude of change was slight (Fig. 6C). This same general pattern was observed in tne discharge basin in 1977 (1977 Final Report: Fig. SC). More species were collected in the discharge basin during each gaarter of 1978 than were collected over the same periods in 1977, although the apparent homogeneity of mollusks was less for the last two quarters of 1978 when compared to t..e s 2 same periods in 1977. Consistently more" species of mollusks were found in the control basin than in the discharge basin throughout 1978 (Fig. 6C). Except for a slight increase during the spring, the number of control species remained relatively constant thrcughout the year. There were more species collected in the control basin during March and June and fewer species collected in September and December 1978 compared to 1977 (Fig. 6C; 1977 Final Report: Fig. SC). I-71
~
The mesn abundance m for mollusks collected using the v e n t. u r i suction method in the control and discharge h basins in 1978 is shown in Fig. 8. Mean abundance decreased considerably in the control basin during 1978,
~
from 220 individuals m in March to 83 indivduals m' in December. There were more individuals collected in the control samples of March and June and fewer individuals collected in September and December 1978 compared to the corresponding samples in 1977 (1977 Final Report: Fig. 10), a pattern similar to that seen with numbers of mo21uscan species (Fig. 6C; 1977 Final Report: Fig. SC). Considerably more individuals were colleaced in L978 in the control basin venturi samples compared to the
~
discharge basin; most obvious were 220 individuals m found in March in the control basin, while only 14
~
individuals m were found in the discharge basin (Fig.
~
8). Mean abundance m declined slightly in the discharge basin over the first three sampling periods in 1977 and again in 1978. Abundance values were similar in June and September of both years but a greater abundance was noted in December 1978 compared to December 1977 (Fig. 8; 1977 Final Report: Fig. 10).
-2 The mean biomass m for mollusks in ventuti samples from the control and discharge basins in 1978 is shown in Figs. 9 and 10, respectively. There is considerable O ,
I-72 e y I e 1
scatter in the data for both the control and discharge basins. Mean biomass in the discharge area dropped from _9~ _a* 20.90 g a in March to 0.12 g m in June. Con;rol biomass was consistently greater than discharge biomass. Mean control biomass was greater in March and Jun' and lower in September and December 1973 compared to these same periods in 1977 (1977 Final Report: Fig. 11). The same trend was seen also in numbers of taxa and individuals. In the discharne basin ther'e was a sharp decrease in molluscan biomass between March and June 1978 (Fig. 10) and also between April and June *177 (1977 Final Report: Fig. 12). However, a sharp increase in biomass between September and December 1978 did not occur during the corresponding 1977 sampling periods. Other Groups Since larger animals are sampled more efficiently using the venturi suction method and smaller animals are sampled more efficiently using the bottom core method, , only those data from the more effective method of sampling 6 are used for comparisons made in this section. Data from s h the venturi suction samples thus are included for t echinoderms, tunicates, fishes and spongas while bottom core data are used for nematodes, nemerteans, platyhelminths and sipunculids. Relative occurrences are given for these groups in Table 1. I-73
Table 5 shows the mean biomass for each of these major groups in the control and discharge basins for each quarter of 1978. Echinoderms, fishes and sponges had consistently lower biomass values in the discharge basin while platyhelminths showed generally higher biomass values in the discharge basin. Following a slight decrease during the spring, echinoderm biomass remained virtually unchanged. Except for a sharp decline during the summer, sponge biomass also remained relatively constant throughout the year. There is considerable scatter in the rest of the data and no other obvious trends over time were noted. O O I-74
4 0 2 1 f 9 5 4 7
,o , s 2 1 6 4 s i 1 7 1 0 ss d D . .
0 0 0 0 dd l 0 3 0 0 0 0 i o l l i u J erd c C nenn npau D 0 8 5 9 2 a p 6 5 9 9 3 g ,i n 3 0 3 3 0 nnss o 5 8 3 9 0 aie C . 0 0 0 0 0 0 hl h , 1 0 0 0 t pss 1 mih r af t es n 3 2 h ,i 3 0 4 5 5 5 t t sm 1 7 onnl s 5 3 2 eae i 1 0 0 srih D . 0 0 0 0 ped y 0 0 0 0 0 0 ufit of ca P ri cl E gd ap S 3 4 7 5 0 cg ,, 6 4 6 7 7 i nss n 8 1 5 6 1 hi mn o 5 0 5 3 0 t r r a C . . 0 0 0 nuee 1 0 0 1 0 0 0 eddt - b or sne r nim 3 9 2 0 7 5 oih e 2 2 jscn 7 0 4 8 0 aae s 7 5 0 2 0 1 0 0 mb , i 0 0 0 rs D 0 0 0 f eoe 0 0 0 0 0 0 0 o gf d r o N 2 ast U
- h ea J 4 5 mclspe m 4 7 9 5 0 0 8 7 9 5 2 7 3 2 ) i mn n 1 0 0 2 0 2 0 0 t d a o 5 6 2 4 0 0 0 0 h sr C .
0 0 gd o 1 1 0 9 0 0 0 0 i nnf eao w i s l t e 5 5 yocl ) 5 9 8 7 0 r r up . 3 6 6 3 6 2 1 dt sms s 6 1 2 0 2 0 1 n ah i 0 0 0 0 0 0 0 soist D 0 mcr a 0 0 0 0 0 0 0 0 0 a r nt uen r g R gi noo A ( ect M sv e 5 6 9 1 5 9 4 3 sk ma n 6 9 3 2 1 6 9 2 0 3 2 9 6 4 9 ssnoh 4 auot c o 8 4 9 4 0 0 0 0 ml t C . 0 0 0 0 0 0 ol d od 2 7 0 1 i oeb n 1 b ms a s an e ndbo , a h a an s t n t e a a eaad e n M t nt a e d t h saaa m a y a i i a t r e h e m o r a
.dD o( ,re e c t a a n l e
l u e n g 5 p st d a h r d i t o en o i c e o t h c n o er .ge n n d i f t r y n e t l h8 nl o i i e i a e t u l e bt7 oe x h c t r m m a p e a ar9 po a c s s o e e l i o h T a1 sc T E A O P N N P S C C s3 iu
~
Seagrass and Macroalgae O Macroalgae Sixteen genera of macr 3 algae were collected from all sampling stations during 1978. Fourteen genera were collected from control stations but only 4 were collected from discharge stations (Table 1) .
~
Table 6 shows the mean biomass m of macroalgae collected at each sampling station during 1978. The biomass data reflect the almost complete lack of macroalgae in the discharge basin. A considerable increase in macroalgae biomass occurred during the mner in the control basin. This was followed by a sharp O reduction in biomass during the fall, resulting in the lowest biomass for the year in the December samples. Total macroalgae biomass m' was consistently greater in the control basin in 1978 compared to 1977, while the discharge basin biomass remained essentially the same (Table 14). Seagrasses Five species of seagrasses were collected from the control basin. These were Halodule beaudettei, Halophila O I-76
engelmannii, Ruopia maritima, Syringodium filiforme and Thalassia testudinum. The discharge basin was entirely dominated by one species, Halodule beaudettei (Table 1) , a i u c. v _ , .. there was very little obvious change in seagrass biomass over time in the control basin, there was a onsi3erable increase in H. beaudettei biomass during the summer in the discharge basin (Table 6). Data on seagrasses and macroalgae were combined to give total macrophyte biomass. Mean biomass m ', standard deviations and ranges for each quarter and bu~in are shown in Fig. 18. Mean seagrass leaf lengths, their standard deviations and ranges were calculated for each species in both basins (Fig. 19). There was a general increase in H. beaudettei leaf length in the discharge basin during the spring, but no appreciable change occurred thereafter. Very little change in mean leaf length occurred in the control basin with the exception of a slight decrease during the fall of 1978. Total seagrass biomass was consistently lower in the ontrol basin in 1978 than in 1977. However, seagrass biomass was generally greater in the discharge basin during 1978 than in 1977 (Table 14). 9 I-77
Mean biomass (grams dry weight) m -2 of seagrasses (SG) and Table 6. mac r oalgae (MA) at discharge (D) and control (C) stations during different sampling periods of 1978. S tation MAR JUN SEP DEC Number SG MA SG MA SG MA SG MA 1C 13.7 47.6 51.8 40.5 0.0 419.4 0.0 21.0 2C 0.0 24.5 0.0 124.1 0.0 363.6 0.1 118.6 3C 20.9 4.8 0.0 0.0 0.2 0.0 2.7 3.8 4C 0.0 390.1 0.0 167.4 21.7 0.6 0.0 121.8 5C 0.0 42.1 0.1 7.4 0.1 14.2 1.3 0.2 Control Mean 6.9 101.8 10.4 67.9 4.4 159.6 0.8 53.1 1D 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 2D 25.8 0.1 41.1 7.6 270.6 0.0 0.1 0.0 3D 42.3 0.0 110.6 0.0 240.6 0.0 45.3 0.0 4D 45.6 0.0 84.1 0.0 147.8 0.0 176.8 0.0 SD 59.0 0.2 35.9 0.0 78.7 0.0 55.2 0.0 6D 1.4 0.0 37.2 0.0 0.0 0.0 0.0 0.0 7D 0.0 0.0 0.0 0.0 260.0 0.0 0.0 0.0 Discharge Mean 24.9 0.1 44.1 1.1 142.5 0.0 39.6 0.0 0 0 I-78
o------o CONTROL 500- c : DSCHARGE oJ t 2 W 3 400-
- s. ~
T Q O v O 300-O 2 _ o__ Q LL) h 200-I b A O r' s
\
g Q P k \
< f f' \
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\
' N, 10 0 - , ,
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( \ a w O MAR 78 JUN 78 SEP 78 DEC 78 9 Fig. 18. Mean macrophyte biomass m~2 in the discharge and control basins during 1978 sampling periods. (Given are means (connected circles) , standard deviations (rectangles) and ranges (horizontal bars) .) I-79
20 CONTROL ~ ~ RU PPI A
-.- -- H ALOPHIL A
--- SY RINGOOlUM
-.-- HALODULE 15 - . .
- 4%3 g p's' N 4 10 -
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- m. , .
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/
10
/ _ _
./
14 ./
/
d 5 r A 0 MAR 78 JUN 78 SEP 78 DEC 78 Fig. 19. Mean leaf lengths (based on num.ber of occurrences) for seagrasses at discharge stations (19A) and control stations (19B) for different sampling periods of 1978. (Given are means (connected circles), standard deviations (rectangles) , ranges (horizontal bars) and number of occurrences.) I-80
Seagrass Monitoring Inside Radials The mean percent cover of seagrasses for the two inside control radials and three discharge radials is presented in Table 7. Seagrass cover in the control area appears to be randomly distributed over distance and time. The percent cover is sparse throughout most of the area, becoming generally more dense near the radials' source. In contrast, seagrass cover for the discharge radials 1DA and 2DA is generally dense throughout the year except for their point of origin which is completely devoid of seagrass. Radial 3DA, which is nearest to and runs parallel with the discharge canal, is almost devoid of seagrass cover along its first half kilometer and is only sparsely covered at the outermost stations. Distribution maps for Halophila engelmannii, Ruppia maritima, Syringodium filiforme and Halodule beaudettei for each quarter in the control basin are presented in Figures 20 through 34. Maps for Haledule beaudettei, for each quarter in the discharge are presented in Figures 35 through 38. Halophila, Syringodium and Halodule were scattered throughout the control area with sparse to moderate percent cover. Halophila and Syringodium were 9 I-81
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...." /
2CA !! f;; 'c 6 J
- l s'/
V PER CENT COVER
<5 5-50 ms f > 50 Q O O.1 i i Km.
Fig. 20. Distribution of Halophila enge1=annti along inside rad 2als of the control basin for March 1978. (Stations monitored at 0.1 Jcn interval. ong . all indicated radials. Absence of shading indicates no seagrass c=".er.) I-83
O
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V PER CENT COVER G
<5 w a 5-50
- ss.ss2'd > S O %
O O.1
- i Km.
Fig. 21. Distribution of Halophila engelmanntt along inside radials of the control basin for June 1978. (Stations monitored at 0.1 km intervals along all indicated radials. Absence of shading indicates no scagrass cover.) O I-84
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. :::. ..y:-
. x ..p. i:
) ,
r, .: . PER CENT COV.:R
<5 50 m:sssa > 50 C o 0.1 i i K m.
Fig. 22. Distribution of Halophila engelmanvit along inside radials of the control basin for Septe:::ber 1978. (Stations .mni- d at 2.1 .b intervals along all indicated radials. Absence of shad:ng indicates no seag: ass cover.) 9 I-85
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. :, . . g&D Il V
PER CENT COVER R <5 5-50
. . m > 50 G O O.1 i i Km.
Fig. 23. Distribution of lialophila engelmanntt along inside radials of the control basin for December 1978. (Stations monitored at 0.1 km intervals along all indicated radials. Absence of shading indicates no seagrass cover.) O I-86
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V G PER CENT COVER b <5 s::: 50 L m.s m > 50 C 0.1 i i K m. Fig. 24. Distribution ci Ruppta cartttaa along inside radials of the control basin for March 1978. (Sta ci - =0.zi tored at 0.1 km intervals along all indicated radials. Absence c! shading indicates no seagrass cover.) 9 I-37
O
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. p. . . .
0 ,,. .- l' o' V PER CENT COVER
<5
?..- _ s-so mwm > 50 %
O O.1 i ; Km. Fig. 25. Distribution of Ruppta curtttaa along inside radials of the control basin for June 1978. (Stations monitored at 0.1 km intervals along all indicated radials. Absence of shading indicates no seagrass cover.) O I-88
X* C w';. ,', 4.. ,.
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'gtQ
s' L'i PER CENT COVER wu < 5 m :.a 5 - 50 www > so G O O.1
- i Km.
Fig. 26. Distribution of Ruppta carttica along inside radials of the control basin fo. c.pte=ber 1978. (Staticns monitored at 0.1 km intervals along all ind::ated radials. Absence of shading indicates no seagrass cover.) 9 I-89
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e/ V PER CENT COVER O F7<5 5-50 m " > 50 ( o o.i n
> Km.
Fig. 27. Distribution of Ruppta marittma along inside radials of the control basin for December 1978. (Stations monitored at 0.1 km intervals along all indicated radials. Absence of shading indicates no seagrass cover.) O I-90
. . . .n.
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L/ O PER CENT COVER ro -
<5
- w. A 5-50 mm*sm > 50 Q o 0.1
= 2 Km.
i Fig. 28. Distribution of Syringodium Et1Lfor:e along inside radials of the control basin for March 1978. (Stations monitored at 0.1 km intervals along all indicated radials. Absence of shading indicates no seagrass cover.) O I-91
, * . . .. .. e. -
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V PER CENT COVER
<5 3:.: 5-50
<.s.n:" > 50 %
0 0.1 1 > Km. t Fig. 29. Distribution of Syringodium tt1tforme along inside radials of the control basin for June 1978. (Stations monitored at 0.1 km intervals along all indicated radials. Absence of shading indicates no seagrass cover.) O I-92
n -
, . , ,(
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, 6 go
,- :.:k6..
.. w-. .:.w r;. .
//
V PER CENT COVER
<5 E 5-50 m ws > 50 Q O 01
- 2 K m.
Fig. 30. Distribution of Syringodtum Et1tfor=c along inside radials of the control basin for September 1978. (Stations monitored at 0.1 Jan intervals along all indicaced radials. Absence of shading indicates no seagrass cover.) I-93
O ~
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g.s's.<YW' y S Q (,
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PER CENT COVER
<5 5-50
.a m > 50 (
0 0.1 i Km. Fig. 31. Distribution of Syringodium E11tforme along inside radials of the control basin for December 1978. (Stations c:anitored at 0.1 Jan intervals along all indicated radials. Absence of shading indicates no seagrass cover.) O I-94
~. . ..
. .. M
' h l..* .
s,.
-h' m ..
..- (
' r .': N. NTAqNAL K_.;,... ~ .e W, . - -
. %;. : ^*. *- .. -
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//
./ _...
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./% .i 2CA !!
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...s,.
q-6 l ,- Vl PER CENT COVER O
<5 5-50 as:s92a > 50 %
o o! i i r(m. Fig. 32. Distribution of Halodule beaudettet along inside radials of the control basin for March 1978. (Stations monitored at 0.1 ]cn intervais along all indicated radials. Absence of shading indicates no seagrass cover.) I-95
O
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r.
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//
V PER CENT COVER G
<5 K"AT:M 5-50 EEZZi > 50 %
O Of Km. Fig. 33. Distribution of flalodule beaudettel along inside radials of the contrci basin for June 1978. (Stations monitored at 0.1 km intervals along all indicated radials. Absence of shading indicates no neagrass cover.) O I-96
. u g.,- .
. n.. , ;
x .- q
. ,. x .
...... [- .
4..
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.. . . ;,..~
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, f.h -
o s ,l PER CENT COVER
<5 5-50 La > 50 %
o 0. I i i Km. Fi g . 34. Distribution of Halodule beaudettel along inside radials of the control basin for September 1978. (Stations monitored at 0.1 km intervals along all indicated radials. Absence of shading indicates no seagrass cover.) I-97
O Note: No Halodule beaudettei found during December 1978 monitoring of inside control radials. O I-98
p' THUMB .
- )
.>. ISLAND.
s IDA . . (,
> 2DA . .,
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, l'
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s
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. , , i - -
q: . . , . _ ,
. . ::.., e PER CENT COVER
<5 '. .
Dis c4 %e e: 5-50 m smm > 50 ? T g,_ Fig. 35. Distribution of Halodule beaudettet along inside radials of the discharge basin for March 1978. (Stations monitored at 0.1 Jan incesvals along all indicated radials. Absence of shading indicates no seagrass cover.) I-99
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*./: v N4't.:0x.X.;.%yq;.
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- g. - *^::. 1:: ;t;X:...... .b. ... p;>X) ..
.;,,. . .3:.. s. - ,
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" '.',.<3' 2- .> . . -
PER CENT COVER .. -
..
- Z ' . l
<5
%cm %*%'.
rs: :a 5-50 . Q Ex+m > 50 0 0.1 Km. .,
- .'- .-{,,
Fig. 36. Distribution of Halodule beaudettet along inside radials of the dischargo basin for June 1978. (Stations monitored at 0.1 km intervals along all indicated radials. Absence of shading indicates no scagrass cover.) I-100
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<5 '. .
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r Fig. 37. Distribution of Halodule beaudettet along inside radials of the discharge basin for Septe:.ber 1973. (5:acians monitored at 0.1 .bm inter.cals along all indicated radials. Absence c! shading indicates no scagrass cover.) I-101
e THUMB'
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- I n7 all indicated radials. ,2sence shading indicatca~ no scagrass cover.)
I-102
present during all four sampling periods; Halodule was not found in December. Ruppia was found almost exclusively within one half kilometer of the radials' source. It was present during all four sampling periods and its percent cover was moderate becoming dense near the shoreline. Outside Transects The outside transects monitoring program was initiated during the June 1978 sampling period, and has been continued in conjunction with the regular quarterly field work. The mean percent cover of seagrasses for the outside control transects and the three outside discharge transects is presented in Table B. Seagrass cover in the control transects is randomly distributed over distance and time and is sparse throughout the transects with occasional dense patches of seagrasses being found (Table 8A). The 17 discharge transects are almost devoid of vegetation throughout the monitoring period (Tables 83, 8C, 8D). The primary exception is station 0.0 on transect 1D8, which had a dense seagrass cover in June and a moderate cover in September and December. Dense seagrass cover along the C discharge transects generally is restricted to the most inland stations (Table SC) .
-103
Table 8A. Mean percent cover of seagrasses m-2 along the outside control transects for June, September and December sampling periods of 1978. Kilometers 3CB ICB 2CB along Sep Dec Jun Sep Dec Jun Transect Jun Sep Dec 0 0 2 0 0 45.8 3.8 0.0 0 2 0 0 0 0.5 0 8.8 8 2.4 0 4 0.8 4.8 4 45.8 0 24 2.4 1.0 16 3.8 11 22 0 30 0 0 1.5 0 20.4 9 0.8 0 10 2.0 0 0 8 0 0.8 0 2.5 0 0.8 0 3.0 s h Table 8A (Cont.) o 4 Kilometers 6CB 4CB SCB along Jun Sep Dec Sep Dec Jun Sep Dec Transect Jun 0 0 45.8 3.8 0 0.8 0.0 0 2 0 5 0 0 30 0 0 0.5 0.8 0 0.8 4 13.8 0 0 8.8 0 1.0 0 0 0 0 0 0.8 0 0 14 1.5 81 1.0 0 0 15 43.8 6 46 0.8 2.0 61 0 26 3.8 46 0.8 0 2.5 39 34 3.0 46 0.8 0 0 9 e
Table 8B. Mean percent cover of seagrasses m-2 along the outside discharge B transects for June, Septenber and Decenber sampling periods of 1978. Kilometers along IDB 2DB Transect Jun Sep Dec Jun Sep Dec 0.0 69 23.6 36 0 0 0 0.5 0 0 23 0 0 0 1.0 0 0 0 0 0 0 Table 8B (Cont.) "[ Kilometers along 3DB 4DB [ Jun Sep Dec Jun Sep Dec un Transect 0.0 0 0 0 0 0 0 0.5 0 0 0 0 0 1 1.0 0 0 0 0 0 3 1.5 0 0 0
Table 8C. Mean percent cover of seagrasses m-2 clong the outside discharge C transects for June, September and December samp1ing periods of J978. Kilometers 3DC 1DC 2DC along Jun Sep Dec Sep Dec Jun Sep Dec Transect Jun 0 41 0 8 0 53 0 0 0.0 46 0 0 1 29 1 0 0.5 93 8.8 13 1.6 0 0 0 0.8 53 0 0 0 1.0 0 0 0 1.5 0 0 0 2.0 Table 8C (Cont.) H I Kilometers 6DC SDC along 4DC Jun Sep Dec Jun Sep Dec Transect Jun Sep Dec 44 0 0 0 46 0 0.0 46 0.0 44 0 0 0 0 0 0 0 1.6 0 0.5 0 0 0 0 0 0 0 0 1.0 0 0 0 0 0 0 0 0 0 1.5 0 0 0 0 0 0 0.0 2.0 0 0 0.8 0 0 2.4 0 80 0 2.5 0 0 0 0 0 0 3.0 0 0 0 0 1.6 0 15 0 16 0 0 0 0 0 0 3.5 16 0 0 4.0
- O e
c000003 e D C p 17 00006 D e 1 8 S n 000000 u J c 0001 00 e D C p 000080 D e 7 S 0 )
. n 0002 06 t u 2 1 n J o
C ( s r t C e c t ge 050505 B ens . e mon 001 1 22 l ol a b l ar a i T T K s s y~ Ojm
Table 8D. Mean percent cover of seagrasses m-2 along the outside discharge D transects for June, September and December sampling periods of 1978. Kilometers 3DD 2DD 3DD along Jun Sep Dec Jun Sep Dec Jun Sep Dec Transect 1.6 66 0 3 0.0 0.2 0 1.6 0.2 1.6 0 3.4 0.0 0 0 23 2.0 23 0.5 0 1.0 66 1.6 3.0 0 0 1.8 4.4 0 3 1.0 0 0 0 0 0 1.5 32 8.0 0 0.4 5.6 4 2.0 0 0 12 0 0 0 2.5 3.0 0 0 0 g Table BD (Cont.) i W o Kilometers along 4DD SDD Transect Jun Sep Dec Jun Sep Dec 0.0 66 0 3 16 0 0 0.5 0 0 4 38 20.8 0 1.0 0.8 0 0 4.8 1.6 32 1.5 0 0 0, 0 0 0 2.0 0 0 0 0 0 0 2.5 0 0 0.8 3.0 4 0 0 3.5 16 0 0 0 0 0
Otherwise saagrass cover i. 'atchy with many areas being completely devoid of v e g e r _i r. i o n throughout the three sampling periods. Seagra 5 cover along the D discharge transects is randomly dia cibuted over distance and time and is sparse throughout ne transects with several stations being devoid of v geration throughout the three sampling periods (Table 8D). Distribution maps for Halophila, Syringodium, Halodule, and Thalassia for each quarter in the control and discharge transects are given in Figures 39 through
- 50. Halophila, Syringodit , and Halodule were found along the control transacts t h r o u g t. a u t the 1978 monitoring program. Thalassia was not .aund along the control transects. Two species of a igrass are found on the discharge 3 transects. Halc ale was found on transects 10B throughout the monito:.ng period and on 4DS during December only. Halophila was fcund on transect 1DB during December. No grasses were fcund on transects 2D3 or 3DB.
All tour species of seagr'ss== are present on the discharge C transects; Halocale, Syrincodium and Thalassia were present throughout the monitoring period. Halophila was found only in Decemb' whilt Halodule was present c.rimarilv alon9 the landward radial 1DC. Svrincodium and Thalassia were found further out along radials SDC, 7DC and 8DC. Many of the stations along radials 3DC through LO9
, D h '
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Fig. 39. Distribution of Halophila engelmannti along outside transects of the control and discharge areas for June 1978. (Stations monitored at 0.5 km intervals along all indicated transects. Absence of data circles at stations indicates no seagrass cover.) I-110
\ Q ( 3 g:;}'
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0 Km. Fig. 41. Distribution of Halophila engelmanntt along outside transects of the control and discharge areas for December 1978. (Sta tions monitored at 0.5 km intervals along all indicated transects. Absence of data circles at stations indicates no seagrass cover.) I-ll2
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Fig. ':. Distribution of Syringodiu= fL1tforme along outside transects of the contro: and discharge areas for June 1979. (Stations mcnitored at 0.5 k: intervals along all indicated transects. Ishsence of data circles at stations indicates no seagrass cover.) I-ll2
I
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Fig. 43. Distribution of Syringodium Etitforme along outside transects of the control and discharge areas for Septecher 1978. (Stations monitored at 0.5 km intervals along all indicated transects. Absence of data circles at stations indicates no seagrass cover.) I-ll4
- O bO y' .' ' ,
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' ll ,C s > Km Fig. 44. Distribution of Syringodium EL1tio =c along outside transects cf the cont:cl and discharge areas Ec: Dece=ber 1978. (Staticns mon:tored at 0.5 i== intervals alcn; all indicated transects. Absence c! data circles at stations indicates no seagrass cover.)
I-115
h 0 G0 -
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em
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Fig. 45. Distribution of Halodule beaudettet along outside transects of the control and discharge areas for June 1978. (Stations monitored at 0.5 km intervals along all indicated transects. Absence of data circles at stations indicates no seagrass cover.) I-ll6
- b '.
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ll,- b~ o 1
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Fig. 46. Distributicn of F.aLodule beaudettet along outside transects of the cont:cl and discharge areas for Septe.The: 1978. (Staticns
- nonitored at 0. 5 k:: intervals along all indicated transects. Absence of data circles at staticns indicates no seagrass cover.)
1-117
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,? g @ > 50 ~.
, ,; // 0 0 0.5
' . ' .. ll ,. C n Km.
Fig. 47. Distribution of Halodule beaudettet along outside transects of the control and discharge areas for December 1973. (Sta tions monitored at 0.5 km intervals along all indicated transects. Absence of data circles at stations indicates no seagrass cover.) I-ll8
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@<5 Q v SCS 9
cu 0 6 5-50 g&
} q.
& > 50 >
o q n.,; ll 0 0 0.5
// ,. O i . Xm Fig. 48. Distribution of Thalassta testudtnu= along outside transects of the control and discharge areas for 7ane 1978. (Stations :nonitored at 0.5 k= intervals along all indicated transects. Absence of data circles indicates no seagrass cover.)
I-119
s LG GO ' 7 .. : Q . . . ._.. .. . g 4Ce ' , , -:*~ C f ,5
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Fig. 49. Distribution of Thalassia testudinum along outside transects of the control and discharge areas for September 1978. (Sta tions monitored at 0.5 Jcn intervals along all indicated transects. Absence of data circles at stations indicates no seagrass cover.) I-120
n gO , t . ca %. . n' - t., 33
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Fig- 3 D5*=riygtion 0* galassi3 teStudLnuD # utSid 4e vf th ogtro a d di S C' " areas #, pece. der 397o. (5t'* gn100#ed a, o. [ w 5cterV3U a10"Y , , in di *'d transects-
~Sence of dat3 'irOlgg at Stat,.ons 5pdicaC*
- Ge'G* coV*T*'
1 121
3DC were devoid of vegetation throughout the monitoring period. Halophila, Syringodium, Thalassia and Halodule were present along the discharge D transects throughout the monitoring program. O I-122
Oyrter Reefs Oysters Two species of oysters, Crassostrea virginica and Ostres equestris, were collected in oyster reef samples during 1978. C. virginica was found on all oyster reefs in both the control and discharge basins while O. equestris was found only on reefs in the control basin (Table 2). Number, shell length and biomass data were recorded for all C. virginica over 2 cm in length in each quadrat. It is expected that environmental stress limiting metabolism and growth might first be apparent in an atrophy of molluscan tissue. Therefore, as a means to monitor the growth or atrophy of oyster tissue, the ratio of mean bicmass (adjusted to a constant s a.n p l e size of 230 oysters to facilitate comparison with the corresponding 1977 data t r e a tm e n t) to mean shell length was plotted for each sampling period in 1979 (Fig. 51). The biomass /shell length ratio for oysters collected in the discharge basin decreased steadily during the year but showed less overall variation than the ratio in the control basin. In the cont.ol basin, the biomass /shell length ratio increased during the spring and fall but fell sharply during the summer (Fig. 51). Nevertheless, the mean weight of oyster tissue relative to the mean shell length is not very I-123
20 o----o CONTROL g 2 ; ; DISCHARGE O v I l-- O Z L1J J 15-J _.J Lij 8 I ' m s' t i
' \
/ \
Z
< s' \\
s' LLJ 2 , \\ d \ O IO- j
) \
g m \ W O \ m
\r w \
< \
\
2 \' 9 , - m Z 5-i p,/- Ld 2 Lt. O O
}<--
Z O
- MAR 78 JUN 78 SEP 78 DEC 78 Fig. S1. Ratio of mean bianuss (adjusted to constant sa=ple size of 230 oysters) to mean shell length of oysters greater than 2 cm in length at ccntrol and discharge oyster reef stat ans for different sampling pericds of 1978.
I-124
different between the control and discharge basins on an annual basis. This was not the case during the 1977 sampling schedule. In that data (1977 Final Report: Fig. 37), the biomass /shell lenath ratio for control samples was always greater than for discharge samples and the general decrease in the ratio seen over the year for 1978 control and discharge and 1977 control samples did not occur in 1977 discharge samples. Furthermore, the comparatively low overall biomass /shell length ratio for the 1977 discharge samples indicates possible inhibition of meat growth in the discharge oysters for that period. For comparative purposes, the overall annual means for the bicmass/shell length ratios are as follows: 1973 Control = 8.9; 1978 Discharge = 9.3; 1977 Control = 9.5; 1977 Discharge = 5.9. Oyster Spat Substantial increases in abundance and biomass of oyster spat occurred in the discharge basin during 1973 (Fig. 52). Spat abundance increased from 90 m in June
-2 to 320 m in December, while biomass rose from 14.08 g m in March to 54.96 g m in December. In contrast, discharge oyster spat abundance and biomass m declined steadily throughout 1977 (1977 Final Report: Fig. 38A).
I-125
OYST ER SPAT $ IS;5 600 - > - < CC
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Abundance and biomass a of spat in the control basin were consistently greater than in the discharge basin. Control area oyster spat declined in both abundance and biomass during the spring but increased considerably throughout the rest of the year. More cyster spat were collected in 1973 than 1977 and, except for June, biomass values were also higher this year than in 1977 (Fig. 52; 1977 Final Report: Fig. 38A). Other Mollusks Twelve species of mollusks, excluding C. virginica and O. equestris, were collected in oyster reef samples in 1978 (Table 2). Ischadium recurvum occurred most frequently on both control and discharge reefs. Odostomia sp. was the only other mollusk (excluding oysters) collected in discharge oyster reef samples. There was n' very little change in abundance or biomass a of I. recurvum and Odestomia sp. on discharge oyster reefs (Fig. 53). Mollusks found on control oyster reefs, however, n declined steadily in abundance and biomass m during the spring and summer but increased again during the fall. The high abundance and biomass values observed in March were largely due to unusually high numbers of 1 recurvum, particularly in one station. As in 1977, the non-oyster mollusks were much more abundant on control reefs than on the discharge reefs. Abundance and biomass of these mollusks were generally greater in 1973 than in 1977 (Fig. 53; 1977 Final Report: Fig. 383). I-127
OTHER MOLLUSKS O ---O CCMTROL g 2000 - . o cisemacc 1750 - S
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Crustacnans It was not possible to control the escape of relatively large decapods which inhabit the oyster reefs. The quarter-meter frames cannot be sunk sufficiently to form a barrier and, with the clumsy prying toola and heavy leather gloves needed to break loose the solid oyster clumps, the capture of highly mobile crabs is fortuitous at best. For this reason, these data are not quantitative and are not treat:3 here other than as additions to the oyster reef taxa list in Table 2. 9 I-129
Zooplankton O The complete list of zooplankton taxa and the relative frequency of occurrence of each taxon, as indicated by the peicentage of control or discharge samples in which it was found, are given in Table 3. The number with its mean, range, and stan.ard deviation for each taxon and total zooplankton, and the mean total dry weights, are presented for control and discharge areas by day, night, and overall for each sampling period in Table B-4 of Appendix 2. A total of 56 zo? plankton taxa were found over the year, with 54 taxa found in the control area, and 49 taxa found in the discharge area. Seven taxa were unique to the control samples, and two taxa were unique to the discharge samples. The discharge area shows a significant decrease in the mean number of taxa found between the June and December samples ( P <. 0 01) , which is reflected by the slightly different diversities seen in Table 12C. This trend towards a lower diversity in the winter than the summer was shown much more distinctly by the 1977 data (Table 12C), in which the fourth quarter diversity was less than two thirds the second quarter diversity. The 1978 mean seasonal abundance accentuates this trend strongly (Table O I-130
3-4), with the June mean being nearly double the December mean. However, a two-sample t test failed to show a significant difference between the means ( . 0 5 < P <.10 ) . This is probably due to the tremendous range of station means in the December data (1,369-114,977, Table 3-4) compared to the range of means in the June data (14,384-87,410, Table 3-4). The 1977 data (1977 Final Report: Table 3-4) show a decrease in the mean seasonal abundance by a factor of 10 between the second and fourth quarters. It also shows the 1977 second quarter range of station means (1,494-105,451) to be nearly as great as the 1978 fourth quarter range. Extremely patchy distributions, as evidenced above, make comparisons between zooplankton data suspect without a very large sample base. A strong faunistic difference between the December 1977, and December 1978 discharge data does occur, however, and should be noted. In December 1977, very few larval animals were found in the samples (1977 Final Report: Table 8), while in the December 1978 samples, larvae were abundant (Table 9). The control area also shows a significant decrease in the mean number of taxa found between the June and December samples (.002<P<.005), which is reflected by the difference in diversities seen in Table 12C. This trend was also seen in the 1977 data (Table 12C), in which the I-131
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fourth quarter diversity was one half the second quarter diversity. The 1973 mean seasonal abundance shows this trend somewhat (Table 3-4). However, the teemendous range and degree of overlap of station means seen in the second (9,471-596,061, Table B-4) and fourth (3,214-415,114, Table B-4) quarter data indicates that a statistical test would not detect a significant difference between the means. In December 1 9 7 ~, , very few larval animals were found in the control samples (1977 Final Report: Table 3), while in the December 1978 samples, larvae were not uncommon (Table 9). Calonoid copepods were abundant in both areas throughout the year. The ubiquitous Acartia tonsa was present in mean numbers from 12,492 to 18,584 individuals, accounting for between one quarter and one half of the overall basin means. Paracalanus crassirostris was the second most abundant calanoid, and exhibited a similar even distribution over area and season (Table B-4). Cyclopoid and harpactaccid copepods were both more abundant in the control than in the discharge area (both seasons). As in J 77 (1977 Final Report: p. I-90), Euterpina a_cutifrons as the most abundant harpactaccid over 1978. However, in the second quarter control area, an unidentified species of harpactacoid (sp. A) was present in greater numbers than Euterpina. This species, 9 however, was uncommon in the December 1978 sampler. I-133
A phytoplankton bloom was not observed in the 1978 samples, as occurred in the discharge area in June of 1977 (1977 Final Report: p. I-90). However, relatively high censities of phytoplankton were observed in nearly all samples over the 3 ear, which may explain the fairly even distribution over space and time of the major filter feeding herbivore groups, the calanoid copepods and molluscan veligers (Table 9). No significant difference in mean number of taxa was dettcted for the second quarter between the control and discharge basins ( . 0 5 < P <.10 ) , but significant difference did occur between the fourth quarter samples ( . 0 F P< . 0 5) . No differences between control and discharge abundance or biomass were detected for the semi-annual means (Table 13). O I-134
Grouped Data Summations The mean annual bionass and, where applicable, the mean annual abundance for 1977 and 1973 of all groups are compared for control and discharge basins in Tables 10 and 11, respectively. Diversity and evenness calculations for 1977 and 1973 are given annually for benthic animals and zooplankton, seasonally for benthic animals and seasonally for :ooplankton in Tables 12A, 123, and 12C, respectively. From Table 12 and Fig. 14 it is seen that the Shannon-Wiener diversity index (R ) is always greater in the control samples than in the discharge samples for both the benthic and zooplankton communities. Evenness also is greater for the control :coplankton and bottom core samples, but discharge venturi samples have a higher evenness throughout the year, than the control venturi samples. As discussed in the 1977 Final Report (p. I-93), the fact that the venturi sampler does not sample annelids as efficiently as the core sampler may bias the venturi evenness calculations. Student's t statistic for the difference between control and discharge means has been calculated for all applicable physical and biological data. The results for the null hypothesis u = g for all sampling periods (Table 13) generally confirm the differences or 9 si.ilarities of the data which have been discussed above in the respective sections. I-135
Table 10. Annual mean biomass (g m-2 except zooplankton, g m-3) for control and discharge basins, 1977 and 1978. Sample 1977 1978 Control Discharge Control Discharge Type Seagrasses wet wt. 132.04 180.60 292.17 2640.54 dry wt. 12.38 22.40 26.50 439.52 Macroalgae wet ut. 188.32 6.48 3101.31 22.94 dry wt. 24.78 0.68 477.95 1.98 Denthic rauna Core samples s wet wt. 106.20 22.44 22.94 17.25 d, dry wt. 38.37 6.43 12.17 4.77 w Venturi samples wet wt. 123.18 11.12 72.29 15.57 dry wt. 46.53 2.42 35.80 8.17 Oysters, Oyster reefs meat wet wt. 589.39 270.88 953.89 504.16 meat dry wt. 79.68 31.50 113.99 60.04 Spat, Oyster reefs meat wet wt. 82.84 70.84 218.16 43.67 meat dry st. 54.94 49.33 144.49 29.85 Zooplankton dry ut. 0.0518 0.1190 0.2107 0.2082 O O O
Annual mean abundance of individuals C 2 (zocplankton C ) for 3 Table 11. control and discharge basins, 1977 and 1978. Sample 1977 1978 Control Oischarge Control Discharc+ h7e ._ 0:.7thic fauna core samples 20,852 7,662 3,475 5,599 389 53 409 79 Venturi samples Oysters, Oyster reefs 132 79 1,019 465 664 176 Spat, Oyster reefs 77 48 8,127 23,048 60,588 37,496 2coplankten 9 I-137
Table 12A. Mean annual benthic animal and :ooplankton diversity (E) and evenness (e) for control and discharge basins, 1977 and 1978. Sample 1977 1978 Control Discharge Control Discharge Type E e E e E e E e Benthic Fauna Core 3.63 0.76 2.82 0.70 3.63 0.78 3.10 0.72 Venturi 3.70 0.78 2.91 0.83 3.55 0.77 3.29 0.88 1.31 0.39 2.51 0.66 2.08 0.56 Zooplankton 1.86 0.52 Table 12B. Mean benthic animal diversity (E) and evenness (e) for seasonal periods in control and discharge basins, 1977 and 1978. 1977 JUNE SEPT DEC Basin APR e E e E e E e E Control Core 3.16 0.81 3.42 0.80 3.01 0.76 3.23 0.78 Venturi 3.12 0.80 3.33 0.85 3.02 0.78 3.15 0.80 Discharge Core 2.56 0.70 2.26 0.70 1.88 0.65 2.43 0.75 Venturi 2.26 0.75 1.75 0.94 1.66 0.70 2.02 0.88 1978 Basin MAR JUNE SEPT DEC E e 5 e 5 e E e Centrol Core 3.11 0.72 3.40 0.79 3.09 0.82 3.07 0.78 Venturi 2.72 0.72 3.14 0.79 2.60 0.74 2.94 0.81 Discharge Core 2.82 0.65 2.65 0.71 2.37 0.66 2.53 0.66 Venturi 2.58 0.88 2.61 0.91 2.14 0.86 2.55 0.82 Table 12C. Total zooplankton diversity (E) and evenness (e) at control and discharge stations, June and December 1977 and 1978. 1977 1978 JU'IE DEC JUNE DEC Basin , e E e E e E e E Centrol 2.43 0.66 1.28 0.37 2.72 0.70 2.30 0.61 Discharge 1.64 0.45 0.98 0.32 2.19 0.57 1.97 0.54 I-138
Table 13. Results of t statistic for d:fference, between control anci discharge means for ea :h sanpling period of 1978 (119: ot = n2; R = Iteject lig; A = Accept flo) . 1978 PARAMETI'It fiARCil Jll!;E SI'PTillisi:R 1)ECi2 Gl'R Teu.perature ("C) R; P<.001 R; .001-P<.01 It; .001<P<.01 A; .5~P .9 Salinity (0/00) A; . 4' P : . 5 A; 0 5< Pe 0.1 R; Px.001 R; P .001 Venturi abundance R; 02< P< .05 R; P<.001 11.- .02<P<.05 A; .5<P<.9 Venturi biomass A; .2<P<.4 R; PN.001 A; .1< P< 2 A; .1<P<.2 Core, annelid abundance A; .4<P<.5 A; . 5< P: . 9 A; . 0 5< P e .1 A; .lcP<.2 Core, annelid biomass A; 4<P<.5 A; .lcPc.2 A; .4(P<.5 A; .9:P H Oyster abundance A; .2'P<.4 A; .2<P<.4 A; .1< 1K . 2 A; 05 P .1 H w W Oyster meat biomass A; .4<P<.5 A; .2AP<.4 A; .5'P<.9 A; .2cP<.4 Itatio raean biomass to A; .1<P<.2 A; .5'P'.9 A; P :- 2 A; .9'P mean shell length Spat abundance A; 05<P<.1 A; .5'P<.9 A; 05cP<.1 A: 05 P .1 Spat biomass A; .05cP<.1 A; .2<P<.4 A; .05'P<.1 II; .02 P .05 tiac rophy te biomass A; .l'P<.2 A; .2<P<.4 A; .5<P<.9 A; .5'P<.9 Zooplankton abundance --- A; .5<P<.9 --- A; .2'P<.4 Zooplankton biomass --- A; .5<PC.9 --- A; .I'P'.2
COMPARISONS WIT!! PRE-OPERATIONAL DATA O In an effort to determine if changes have occurred in community structure since the commencement of Unit 3 operation, field and laboratory observations have been compiled to form a data base for comparisons with pre-operational studies. The pre-operational studies were undertaken in 1973 and 1974 by investigators at the University of Florida and the University of South Florida. These were compiled into a final report submitted to Florida Power Corporation in 1974. Due to the vast differences in fielc collection times, locations, techniques and data analysis, only a few groups of data within the 1977-1978 sampling periods are sufficiently similar for direct comparison with the pre-operational study. These groups include mean macrophyte biomass and diversity by taxon; oyster and spat abundance and biomass on reefs; venturi abundance and biomass; and salinity and temperature. There is no adequate comparative data available for this area prior to the initial start-up time of the two coal-burning plants in 1967. By the time of the pre-operational study, the discharge and control basins apparently had evolved into quite different physical and biological systems, probably in response to man-made O I-140
changes. These include a long history of physical @ separation of the two basins by the present jetty system, cutting and redirecting of tidal creeks, and thermal effluents from two fossil fuel plants which had been entering the discharge basin for several years. Direct comparisons between the two basins, therefore, are complicated by many other factors besides the operation of Unit 3. To further complicate comparative analysis of pre-operational, 1977 and 1978 data, Unit 3 was inoperative for nearly 7 months, from 3 March 1973 to 29 September 1973. Therefore, comparisons of pre-operational data with both the 1977 and 1978 data on the separate basins seems to be the most suitable approach to determination of possible effects of Unit 3 operation. Comparisons of mean seagrass, macroelgae and total _o~
=acrophyte biomass n by basin and seasonal period are shown in Table 14. There was very little difference in total macrophyte biomass between the pre-operational (van Tine 1974) and 1977 studies in either basin. However,
~
total mean macrophyte biomass m consistently was greater in both basins in nearly all 1978 sampling periods compared to the pre-operational and 1977 studies (Table 14). I-141
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9 Table 14. (Cont.) Sampling Control basin Discharge 11asin Taxon Period Pre-op 1977 1978 Pre-op 1977 1978 11hodophy ta 1 32.2 25.9 56.0 4.4 1.0 0.0 2 17.1 24.5 16.0 4.2 0.0 1.1 3 -- 11.0 0.1 0.1 0.0 0.0 4 15.7 3.2 6.4 0.5 0.0 0.0 Annual 20.8 16.1 19.6 1.5 0.3 0.3 y Phaeophyta 1 6.9 3.3 30.3 0.1 1.8 0.01 H 2 6.4 5.4 42.8 0.7 0.0 0.0 C 3 -- 20.2 0.0 (0.2) 0.0 0.0 4 12.2 6.0 45.8 8.5 0.0 0.0 Annual 9.8 8.7 29.7 2.8 0.4 0.0 Chlor ophy ta 1 3.2 6.6 15.5 0.0 0.0 0.02 2 14.6 10.8 9.1 2.4 0.0 0.0 3 -- 5.3 159.4 0.0 0.0 0.0 4 1.9 4.3 1.0 0.0 0.0 0.0 Annual 4.2 6.8 46.3 0.3 0.0 0.0
- Sampling Periods 1, 2, 3, 4 correspond to pre-op samples of spr ing, summer, fall, winter of 1973-1974, 1977 samples of April, June, September, December and 1978 samples of March, June, September, Deceruber.
The overall m"crophyte composition of the control and discharge basins also has changed dramatically. During the pre-operational study, the control basin total macrophyte biomass was composed ot 69% macroalgae and 31% seagrasses. In 1977, the basin remained relatively unchanged. In 1978, however, the total macrophyte biomass for the control basin was 94% macroalgae and only 6% seagrasses. A different pattern of macrophyte change occurred in the discharge basin. During the pre-operational study, total macrophyte biomass consisted of 77% seagrass and 23% macroalgae. By 1977, although there was little change in annual mean macrophyte biomass, seagrass accounted for more than 98% of the total macrophyte biomass. In 1978 the total macrophyte biomass for the discharge basin was more than 99% seagrass. This dominance of the macrophytes in the discharge basin was due to the almost exclusive presence of one species, Halodule beaudettei (Table 1) . Mean macrophyte diversity was calculated to give the
~
number of species (or genera) m in order to compare with pre-operational data (Table 15). There was no obvious difference in mean seagrass or macroalgae diversity in the discharge basin between the pre-operational and 1977-1978 studies. Mean annual O I-144
seagrass and macroalgae diversity decreased slightly in the control basin, however, between the pre-operational and 1973 studies. Comparisons between pre-operational, 1977 and 1973 oyster reef data, including oyster and spat mean abundance and biomass, are shown in Table 16. Although a considerable decrease in oyster abundance and biomass occurred in the discharge basin between the pre-operational and 1977 studies, an increase in abundance: and biomass followed during 1973. Mean oyster abunde.nce and biomass for 1973 are similar to pre-operational values. Spat abundance and biomass also decreased in the discharge basin between the pre-operational and 1977 studies. Summer 1973 spat abundance and biomass d e c li r.e d even further while winter 1978 data showed substantial increases. No obvious changes in oyster abundance or biomass occurred in the control basin between the pre-operational and 1977 studies. However, while there was a slight difference between 1977 and 1978 summer abundance and biomass, a considerable increase in abundance and biomass was noted during winter 1978. A similar pattern was observed with spat abundance and biomass during winter 1973 in the control basin. In contrast with the oyster I-145
Table 15. Mean diversity
- by taxon, sampling period ** and basin for pre-operational, l?77 and 1978 studies, g Sampling Control Basin Discharge Basin Taxon Period Pre-cp 1977 1978 Pre-op 1977 1978 Total 1 6.0 7.4 8.2 1.9 1.4 1.3 Macrophy te s 2 7.8 6.4 4.0 1.5 0.7 1.0 3 --
5.8 1.6 0.5 0.7 0.7 4 7.5 5.6 4.6 1.3 0.8 0.6 Annual 7.1 6.3 4.6 1.3 0.9 0.9 Total 1 1.3 1.6 1.0 0.9 0.6 0.7 Seag rasses 2 2.1 1.0 1.0 0.7 0.7 0.7 3 -- 1.2 0.8 0.4 0.7 0.7 4 1.9 1.0 1.4 0.7 0.8 0.6 Annual 1.8 1.2 1.0 0.7 0.6 0.7 Total 1 4.7 5.8 7.2 1.0 0.9 0.6 hacroalgae 2 5.6 5.4 3.0 0.8 0.0 0.3 3 -- 4.6 0.8 0.2 0.0 0.0 4 5.6 4.6 3.2 0.6 0.1 0.0 Annual 5.3 5.1 3.5 0.6 0.3 0.2 Rhodophy ta 1 2.8 4.2 4.6 0.8 0.6 0.1 2 4.3 2.6 1.4 0.7 0.0 0.3 h 3 -- 2.8 0.2 0.2 0.0 0.0 4 3.6 2.4 1.4 0.3 0.1 0.0 Annual 3.5 3.0 1.9 0.4 0.3 0.1 Phaeophyta 1 0.6 0.4 1.8 0.1 0.2 0.3 2 0.5 0.8 0.6 0.0 0.0 0.0 3 -- 0.4 0.0 0.0 0.0 0.0 4 0.9 0.6 1.4 0.0 0.0 0.0 Annual 0.8 0.6 1.0 0.2 0.1 0.1 Chlorophyta 1 1.3 1.2 0.8 0.1 0.2 0.1 2 0.9 2.0 1.0 0.1 0.0 0.0 3 -- 1.4 0.6 0.0 0.0 0.0 4 1.1 1.6 0.4 0.0 0.0 0.0 Annual 1.1 1.6 0.7 0.0 0.1 0.0
- Number of species m-2 except number of genera m-2 for macroalgae of 1977 and 1978 studies.
** Sampling Periods 1, 2. 3, 4 correspond to pre-op periods of spring, summer, fall, winter of 1973-1974; April, June, September, December 1977; March, June, September, and December 1978.
O I-146
Table 16. Comparative oyster reef data for the pre-operational, 1977 and 1978 studies, for sunaer and winter sarapling periods.* Data presented are for 0.25 m2 quadrats. Sample Period Control Discharge
'rype Pre-op 1977 1978 Pre-op 1977 1978 Oyster abundance Suramer 260 174 235 157 66 137 Winter 124 172 422 207 74 173 Oyster meat dry ut. (g) Sumiuer 28.4 28.4 38.2 26.0 5.7 21.7 H Winter 12.0 18.9 38.1 25.8 8.1 21.2 H
Spat abundance Summer 608 150 33 187 41 22 $ Winter 031 30 378 49 8 81 Spat dry wt. Summer 65.6 12.8 8.8 126.0 12.6 4.4 (9) Winter 99.3 15.7 58.2 20.6 2.3 12.5
- Suruner : pre-op control = July & August 1973 pre-op discharge = July 1973 post-op control & discharge = June 1977, June 1970 Winter: pre-op controi = January 1974 pre-op discharge = December 1973 post-op control & discharge = December 1977, December 1978
data, spat abundance and biomass showed definite declines during summer 1978, continuing the trend reported for h summer 1977. Comparisons between pre-operational, 1977 and 1978 venturi suction samples for the control and dischcrge basins are shown in Table 17A and 17B, respectively. Means, standard deviations and 95% confidence limits are
~
given for annual abundance m and annual wet and dry
~
weights m . Abundance and biomass of contr 11 basin samples collected during the 1977 study were an order of magnitude greater than in the pre-operational study. Mean abundance in 1978 was comparable to the 1977 value; biomass increased by a factor of 3 over the pre-operational study but was generally less than in the 1977 study. Results of the t test for differences between the pre-operational and 1978 means show significantly that annual abundance and biomass are greater in the control basin in 1978 when compared with the pre-operational study (Table 18). Mean abundance and biomass of discharge basin samples were greater in 1977 than in the pre-operational study (Table 17B) but were not found to be significantly different (1977 Final Report: Table 17). The 1978 mean abundance and biomass in the discharge basin increased O I-148
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m r e h o P 7 2 4 7 0 d t r D nf S 6 5 3 5 4 d e 0 2 3 r b n a i d l s n l a 2 1 1 7 8 a ab r _i _ 4 1 2 2 1 t u el 7 2 1 2 2 v o = O r t D n e S
. o e t t r A c r e
c h h u ; 7 n g g t y n 1 e t a i i a t a h e l d e e r i ) e et m an w w e) n 0 G m l a uu ) ) pC i 0 b r ao r a nb na t 9 e( y9 r( m" e( l Tf P A 1 1 D T S a o/_(_ s-7Um
t y 2 L 7 9 2 3 8 2 7 6 1 2 3 9 8 7 2 i 1 n i l a 8 8 4 1 5 s 1 . . L 8 2 0 6 3 d 2 - 2 2 n 8 a 7 9 e 1 1 r 1 8 0 6 u D . . t S 0 2 2 4 5 a 3 3 2 r 1 e p m e 3 6 2 7 6 t . i 9 5 8 7 5 d 7 1 2 2 n a s e 4 6 2 6 1 l . 2 . ps L 2 9 3 0 7 me 7 1 3 2 ai . sd s u l it a r s 8 9 3 5 6 v u 1 r t 8 L 7 0 1 7 5 e n7 2 2 2 t e9 7 n v1 7 i 9 md 1 e on 2 6 8 9 0 c r a D n f 2 7 7 S 8 5 1 2 3 4 2 d i f e
- 9 m1 n o
sd 1 2 3 0 4 c r n . . ea i 0 0 2 9 6 % t 5 1 2 2 5 el 9 ma an = r o ai 2 pt 9 5 6 4 2 L a 2 . , yr _L 3 3 2 9 7 1 t e 5 1 2 2 L i p no ; u - n me 1 6 7 8 0 o mr pL op 1 2 1 i 4 6 6 t c O 3 2 2 a m - i co e v i r r e hf P 7 2 9 3 7 d t D nn S 8 8 1 5 2 d ei 5 r b s a a d l b _ n l _ 0 9 1 1 6 a ae r g _R . . t 3 8 2 8 6 s er 4 2 2 va = Oh c D s e S
.i e t t r 8d r c :
h u ; 7 e n 19 g t y n 1 e t a 1 i a t a h e ld e e r i ) e et m an w w e) n oo l b r ao Tf r P a a A uu nb na H t 9 e(
)
D y9 r
)
( T pC mO e( i l S a (
/
i m
= 9 TC
over pre-operational and 1977 values (Fig. 173) and the d i f f e r e r.ce between pre-operational and 1978 mean biomass ( dry wt) and abundance was found to be significant (Table 18). The differences in annual mean temperatures between the pre-operational and 1078 studies were 3.7 C in the control basin and only 0.4 C in the discharge basin (Table 17A and B). There were no significant differences between the means of either temperature or salinity for the pre-operational study and the comparable means for either the 1977 or 1978 post-operational studies (Table 18; 1977 Final Report: Table 17). Figs. 52-55 show the range of abundance and biorass based on two standard deviations of the 1978 quarterly means in cont--' and discharge venturi samples. For comparison, the quarterly means for the same parameters from the pre-operational study are superimposed. All pre-operational means with one exception fall within two standard deviations of the 1.178 means. In that exception, the mean pre-operational benthos biomass for the discharge basin samples was slightly greater than 2 standard deviations above the corresponding 1978 mean. 9 I-151
9 Fig. 54. Mean a?'indance m~2 from venturi control samples of the ore-operational study superimposed over two standard devia tions of c.b comparable mean from the 1978 stud) . O I--152
1,6CO i,4CO-CONTROL B ASIN e-----9 P RE-CPERATONAL MEANS 26 CF 1978 VEANS N 1,2CO : I 2 cn J
< I,000-D Q _.
Q Z_ 800- - cc W CD 2 6CO- a 3 Z Z W 400- t 2 \ 200- .
+ . , _ ,.
+ ------*
O l I l l 2 3 4 g QUARTERLY SAMPLING PERIODS 1- m
O Fig. 55. Mean abundance m~ from ' *" ^ 3ri discharge samples of the pre-operacional study superimPCsc over two standard deviations of the comparable mean irc~ the 1973 Stud 9-0 I-154
D I S CH ARGE 8 ASIN t- - - - --9 P RE-CP ER ATION AL 9 MEANS ; N 600- .
- t2 # F 1978 CNS 2
cn _J
< 500-o o
o z 4CO-t w ca 2 a 3CO-z z W 2C0- ! 2 i 100-
,,A
,/
~~. ,~~~ 4 ,s' 1, , -
0 I n I 1 2 3 4 g QUARTERLY SAMPLING PERIODS I-155
O Fig. 56. Mean biomass m*2 from venturi control samples af he pro-operational study superimposed over two standard devia:Lons of the comparable mean Ercm the 1979 study. O I-156
CONTROL BASIN
&---M P R E-CPERAM4AL MEANS 12 cr OF 1978 MIAN S 6 -
N I 2 3 C O g 200-(n 2 O_ Z
< \CO- )' !.LJ .,
2 (pd'~,~~~*
.4 I I I i i 2 3 4 O QUARTERLY SAMPLING PERIODS
_=
O Fig. 57 Mean biomass m~E from venturi discharge samples of the pre-operational study superimposed over two standard deviations of the comparable mean from the 1978 study. O I-158
DISCHARGE BASIN
#----4 gegturem
, " 12 e CF 1978 MEANS N
I 2
\
g 10 0 - ; 3: CC o g 80-v m m 2 60-o__ Q Z
< 40-to 2 .
20-
#------ +_._._______,,
o i i i i i 2 3 4 g QUARTERLY SAMPLING PERIODS I-159
JISCUSSI0ti A!ID C 0 tI C L U S I O !I S O. Differences between the control and discharge areas which existed pr t ,r to the operation of Unit 3 have been discussed in the 1977 Final Report. These physical differences continue to have major effects upon comparisons of at least the benthic communities of the two basins. For this reason, the basic factors associated with the variable characteristics of the two basins are repeated below as an introduction to the discussion of the 1971 results. Significant divergences in physical conditions and in the structure of biological communities probably commenced with the early jetty construction and resulting alteration O of current and sedimentation patterns. These processes have acted in concert with long term effects of the total pl an t operation over the past 13 years to provide che present unique er.vironments observed in the separate basins. Since temperature, salinity, current patterns, bottom types and benthic macrophytes are all widely divergent between the two systems, the differences recorded in population parameters of the various faunal communities are dependent upon interactions of all the various factors and of the divergence of the two environments. O I-160
Effects which may bc dae to changea in plant operatt ans, therefore, canact be detected by simple comparisons between contr31 and discharge areas. Only by comparing differences in degree of change cetween the two areas over subsequent annual periods can one reasonabl; expect to detect effects of changes in plant operation. To some extent, the data presented in this report for the first two consecutive years of the technical specifications study have begun to suggest pcssible effects of plant operation. In the 1977 Final Report, an additional obstacle to impact analvsis of the effects of Unit 3 operation was a tientified in the differences in technique which complicate the evaluation of differences between the pre-operational and tne 1977 study. The long period of shutdown of Unit 3 during 1373, n0 wever, now allows direct comparison between an operational and an essentially non-operational year with i den tical techniques (the 1978 period OC shutdown affected sampling results for the two warmest sampling periods of June and September). During 1973 the mean temperature dropped 1.3 C and n tne mean s a l t .'. t t y dropped 0.3 "/co from the corresponding 1977 means for the discharge basin (Table 173). :ielther temperature nor salinity in either basin for 1377 or 1973 O
& 10,.
varies significantly with these parameters during the pre-operational study (Table 13; 1977 Final Report: Table 17). However, for changing physical parameters such as temperature and salinity, it is unlikely that measurements taken over only four weeks of a year would generate valid annual means. Fortunately, quarterly means of biological data do not vary with short-term variations as directly as do the physical data of temperature and salinity. Comparisons of the biological parameters, therefore, are the more reliable indicators for impact analysis. The differences between 1977 and 1978 biological parameters are described throughout this report. In general, control and discharge macrophyte biomass, discharge venturi abundance and biomass, as well as discharge oyster abundance and biomass, increased considerably during 1979. The ratio of mean biomass to mean shell length for the ubiquitous oyster Crassostrea virginica may have value as an indicator of short-term perturbations of the discharge environment. This is because the short-term variations in meat weight detected by this method reflect ambient environmental conditions, either of food supply or stress O I- 162
factor;, or cath. Ia generai, the ratia valle3 for June, 3eptember and D?cencer 1 9 7<3 !! i not show tha substantial variation 'etween c control and discharge casins that saa apparent dur_qg tha .377 operational period 3inc3 th+ lack of effluent from Unit 3 during 1:s non-operatiana; period of 3 March 1373 to 29 3eptember 1978 was the only apparent major phy3 Leal parameter which was different between the two years, it suggests that the lower meat weights of oysters in the discharge basin dur ng June, September and Decamber 1977, when compared to the corresponding periods for 1973, may have been a result of the operation of Unit 3. Unfortunately, the ratio value3 for March 1973 and April 1977 cannot be compared because control temperatures for April were already about 3 C above control temperatures for March, presumably due to acasonal change. Although there were other substantial differences between 1977 and 1973, for example in macrophyte abundance and composition in both bacins, and in core 3amples of the central basin, ther2 were no other clear suggestions that the operation or non-operation of Unit 3 was a specific causatire factcr. It is anticipated that at the conclusion of the third year of this study, results from the three canaecutive
- xjs
fears should begin to show definite trends between operational and non-operational periods of Unit 3, if the environmental impact of this unit's operation la in fact significant. O O I- 164
n, . - , c- .o. e ,1 C ea-Connell Metcalf 5 Zdd,. , 1373. Crystal River Commun i t-; S tr uc ture S t u d .? _I _n . C r v. a t a l River Unit 3, Annual Environmental Operative Report, Vol. 1 'io n-radiological, 1-14-77 to 12-31-77, Florida Power Corporation. Cushing, C.E., Sr. 1961. Limnol. Oceanogr. 6: 439-430. Florida Power Corporation. 1974. Crystal River Power Plant: Invironmental Considerations. Fi lai Report to the Interagency Research Advisory Committee. Vols. I-IV. Mason, N.T., Jr. and P.P. Yevich. 1967. The use of phloxime 3 and rose bengal stains to facilitate sorting benthic samples. Trana. Amer. Microsc. Soc. _8__6 - 221-223. Van Tine, F. 1974. Report D: Comparisons of the benthis flora in estuaries adjacent to the Crystal River Pow._ Plant: Environmental Consideraticas. Final Report tc the Interagency Research Advisory Committee. Vol II. I-165
Appendix A Common and Scientific Names of Economically Important Species f Frca 1977 Collections Common Name Scientific Name Virginia Oyster Crassostrea virginica Horse Oyster Ostrea equestris Bay Scallop Argopecten irradians Blue Crab Callinectes sapidus Pink Shrimp Penaeus sp. Acorn Barnacle Balanus sp. O I-A-1 O
9 Table B-1. Basic st at ist ic:, for each taxon and wet and dry weights for each major group f ri,a bo t t out core munples of 19/8. ( U t.h t L L wtTCALF 6 tDOV i Iff 5T Ust AMit H HANfN - C i l". T *
- 4, >>PuMT 6 0ia OW Lb A L,L rit I [ ? t le. C f lW F' t idne t L' A P'!s t P CON t*0H ATI(He CLM4alNITY STHUCTupf S T b ill AT ChV.STAL HIVEP PG-tH Pl. A N T
---- - -- - h u M t4 6.H IH' I Nl11 V I ptj Al,6------* =
- - - - - - - P F s< .s tiuAkt MtTEH------ ----WhT WElGHT---- ----DHY mtIGHT-----
N Mt A% PANGF 51D Ot V 10 T A L, ptAN/M2 TOTAL WFAN/M2 IAtos Pu t t,um C at i.*:Nith4IA 0.637 0.127 0.05442 0. O l u lf Cl. A % 9 ANTHH/HA H4to. SP. JS. '. . ! 0.- 25 14.39 P H i t, U .I A %t'Nt t a l % f Ht 3 0.662 0. ! !2 0.099h 0.0199
. HNin. SP. $704, llev.W 76.- 346). 1361.2a Pn y s ii. %taturthta 2.159 0.428 0. 4 ) 2 'd 0.0666
*u t o , sv. 1u44 J u d . ta 151.- 180 4 5. ht H ensbu* Sltrmchi,a 2.l6S 0.41) 0.2776 0. 0 6 fe l.
a ou o. sP. iO2. 20.4 0.- 25 n.n l H P H y t.u as Angt t,lon 112.424 2J.464 43.6019 6.7604 C l, A s s OLIG.irnat T A U a li). SP. 7410 14eJ.0 J ea l . - 44S6 1691.)H Cl, A $$ t*Hl. V t' ++ A F I A U4to. SP, St. 10.2 0.- St. 22.78 9AMILY A = P H A H t' T I D A t: Coht 40 lointo l ouoo =or yo.ahn. LA67 rait;E IN ELANCH w&S tul0008) PAO [ A ttihild t Cout 4 0 6 0 0 H 010110 0 25 S.! 0.- 2$. 11.39 I a t 1. ] h w A MarusAT4 JS. b.1 0.= 25 31.JV tAdl~ Sur '4 6CCf I t' A t: - A .a t h i C U L A U. 'siATA St. 10.2 0.- St. 2J.7d e A M ; L, V 4W& dei 1.!- > - AwAn.tLA :8I. W 12, s', 0.- St. / *. t A 41 a c a e li, ' r e l i t a,[24 (>..: .A 1477 s9h.+ .i, '$ ..JS
. )i n = & S ['i s r a i i nN h l t N '. i : *+ 0 412.0 ., . . >l.11 hd
% tvH mvoiras PLarfPHoClus IS). 30.6 0.- St. 16. 11 SU
.i s i . . ,. r . 4. vi.7 0.- 204, n . e. e. Sy,
> A 'i l ? , y CtweaTEinAE f.I J -
=*
t&MiLy T a4 A w w a M,
- 1+ N I J 4 l.a >
1846 219.2 127.- 18J. l19.44 7-% r-j w a p ia.t i f A S A Ne'ilI NF A
. 76 15.3 0.= 2S. ll.9S , n1
> A ** i L V i 1. A .*
- f. l . I t . > 6* I L) 8 f 25 II.)W L -[G t;_ _3 r ! .e. im 16
- e fra 25 S.1 0.-
C;M t aa t e : . sl al f t At
- a v. i,aa s .> . 102, s0.4 0.- St. al.il s o i s. g a lnu t n ae p
)S 7 76 I t' . 6 2 'J G16 Il s O* t h l F A l.P A 17 bi . 0.-
* > A u f f, f I,H
- i w l = t .* > 10 4 >
i l ' * ** .* i =
- w 6 t. W. 2S. S.1 0- 25. II.JV e A" s i y 'a A v.t i o n o t e An*i o. 6etieno .* A e he J. IlJ.4 o.- IS7 154./l r 4 4 t i. i a a t,o Al- l o a t a s ! . i i e4
- l.l. A w .H 'U S A / ti S ) . 570.4 16.- IS74 bJS.*?
..< u l o A N Y C a l 5 A
- L H ! (. A N A jll. ti b . J 0.- 1)H. 'd 1.1 1 e A m a .. .*ueinat e ,*4, 1: ruiasni lit. n r. . / o.- 2SS, 107.44
Tab 1e 11 - 1 . (Cont.) Cu%htLL 4tTCalf & tCDY
=Asl* - Di= T w ot wt Pow T t op f lia s T QuawTtR morrow Cowt 6LudlDA POwfM COwPOwATInh OW6 HALL
- COudUNITY STWUCTUwt Sluoy AT ChfSTAL HIVEN PO=LN PLAhT
--------husetw or !=DivinUAL6--------
-------PFa SGdAHE mtTfN------ ----et:T uflGHT---- ----0RY at&GHT-----
IAnow 4 mean panGE STD btv Total alan /m2 TOTAL mEAh/m2 statis tALSA 76 15.3 0.- 76 34.16 a 4 t h. SP. 25 S.A 0.- 25. 18.19 e A = l e. v omorninAF ONuPHIS %>Nul05A 4202 h40.3 16.- 193$. 901.57 eAalla q w H l % I 19 4 6 MAPlovtot. ort.oh Wdh45705 14St. 290.3 102.- 681. 2tS.7s
=Al=5htIS SP. 127 25.S 0.- 127 S6.94 SColoPLOS HUNNA 357 78.) 0.= 2SS. 107.lJ 0110 sr. --
St. 10.2 0- St. 22.78 - p A = l t. : P&uAoNinat Aw!ClutA P H 11.H 14 A t 1630 125.v 25,- 5)S. 207.97 r4 AwiClot.A f a s t,ow l 1604 32u.9 16.- 189 302.70 i Axictnta SP. 16 IS.) 0.- St. J2.18 $' PAwAnals SP. 1299 JS9.7 2S.- 7 16 309.49 ta o w l !) . AP. 76 IS.) 0.- 2S. 11.45 F A = l t.1 P HI t Lion)Cll. At E r > O *. 6 He it worHD A 2S. S.1 0.- 25 11.3v FAmlLY Pot C i toc H A r. r l p A E PUtCILOCHAtTuS JOHmsoN1 4e4, 96.u 0.- 431 168.34 6AaILY POLINdlDAL _ _ _ _'F'I I f.telooworoh hP. 25 S.8 0.- 25 18.39 Y[ FAalLt 5 A M P Ll. l D A t S, Chow Dant HI 1426 284.2 lie.- 407 v1.b) ICC tandlCAA hP. 44be. evt.J 30s.- 1910. 644.W7 ((;- sabeOLA plC=OPTMALMA St. Su.2 0.= St. 22.74 cr,- - - UNiu. SP. 76 15.3 0.- St. 22.79 c;kh; FAeltf APlagloat PAWAPhlo40SPlu PIN 4ATA 240 Se.0 0.- 204, 61.3u g___
*~
pot u o iw A .> h sit w l 4227 e4S.4 25.- 1922 1720.7% , rw lomosPl ) Mr. itwoHM A4CH l 4 luwe. 336.9 bl.= 942 )#4.26 7-SCHLtLtvis SquamATA 102, 20.4 0.- 51. 21.31 r s ta t.pLu8Plo er me n t CTI 15). 30.6 0.- 127 55.21 _ ONIO. AP. 30e. el.1 0.- 178 78.82 tA=lLV % y LLib At c~ tsoGoNf othPAR 4660 912.0 2SS.- 2345 U20.15 6 f l.4. t h oP. 4876 blS.2 St.- 348J. 1444.S5 C UNIH. SP. 331. +6.2 0.- IS). 5s.62 F A r t i,5 f t we nt'Lt.ID AE
*%nvaonwANCddh 6AwGolmEus 2S. S.I 0.- 25 II.J#
LfNjlLA At H A IS79 315.W 0.- 7tl. 344.Jv PisrA CwistATA 2SS. SG.9 0.- 17W. 74.24 PleTA PALa&TA 306, 61.1 0.- 2SS. 110.41 u91u. 3P. 127, 2$.$ 0.- 16 Jt.19 w votboe =oseusCA ( l. A s s A = i. .< t .. e o w A 4.4aS 0.hel J.Illo 0.4222
*A-10s ARAC 1theCH[T peIpAt,
- ACanfaotalfo*A F Wbm A* A 2S. S.8 0.- JS. 31.j9 t A = I I. y ( No m. u H I Ts us l H At 15t H e. 'C H i lii s P A P I Lt.osD % mho. 17).J 0.- 71 ) . 106.32 O O O
0 l'a h I e 11 - 1 . (Coill . J t o h r. t L t. = > TC A t t 4 troy n A 31 s, - ri s '. r sv el, ht 6 sew? I siw FIH57 duAN T t.H eolina C' hi r. f t.* ** t D a Pil= t w ChrPoH4TloN ih t H & ll, c f.N e u '4 ! T f 5 T ,t o c r u es t Sruoy &T CPVST4L HIWe H i La w r el PL A r4 r
--------nowntH ot I N ii l v l e,u A t,3 --------
-------etu su o a w t' atitp - --- ----.6T mt;lCnT --- ----t1Ny aftGUT==---
1A:04 u mt AN w a s. i,t sin t;tv l o i a l, e6AN/w? TOTAI. MEAh/m2 Cl ass NidALVIA 9. tI S S 1.911 S.9766 1.195)
- t. 4 t. w i r A wi; l aim isoH roN I 25 5.1 0- 25 11.39 t 4m ti y ('AwotfIoAt C A *< li f T 4 = t H A t l.lis t o A N A 7h. 15.4 0.- 76 64.th
&A*1Ly s.t l' r e lf. I la A >
S Y Me t t.a et, A mot. A r A I tt l e . dl3.9 76.- 4 t6 4 , ll1.b> 6ArlLt 4 f f i t. l f r a t a d sr o t.I's L 4 I t td 4 6. I s 2S. S.) 0.- 25 11.39 ttafty s>=>t ! n a t'
. ma - soat l 25 S.I U.* /S. 11.19 a 4 " f l. Y f e l. l. I N 16 t r i 1. t w a w. $1 '
O.- 2$. it.
' tass i, a . i . . o . n a
- 6. l fl 6 1.29'e *.0042 . t, n 2 a e a= il actes<l. .e e i* +.' l e a e anae 'ot, A T A is). 71.) 6 . . s tl e A a l t. , n A = 1.. . o l o a t we=1 ote a sv. 127 25.S 0.- 76 16.01 t am it : che ctunt catto= sr. 25 S.) 0.- 25 11.19 f4=1Lf C H t P t 1101, [ 16 A t.
re t v i E'il.6
- 4C.o o6 4 48. 19.2 0.- 2%. 11.wb -)
Cwt 68thML4 i LANA 25 $.1 0.- 2S. II.19 t A N 11.1
- A H <, I ;+ t L i ! is A t.
... A a.io. t w a o v ol. I t t iwee lb 407 b .b C.. 10b. 12 6 b e. ,-4, a a w G i .4t i f. A A v ! C 1 'e 4 25. 3.1 0.* 25 II.39 '
- A N G l h t 1. t. 4 1. 4 d & L L t f A N A 25 3.1 0.= 25 11.39 t a m t t.f v v $8 T a l ot I.t. f u A t.
.o s i514
- t A NP. g IS). 30.6 0.- 102, 41.b4 Qgf' T o w + ia l s.t. a u. St. 10.2 v.- 25 I!.9S c_ ; ; .
6 A a l l, y J 1 1
- l m e 6.4. i t, A t.
ft1:.osto"A s i' . 25 S.1 0.= 25 II.!d (XC
~C
(. ^ 2 p,+ v t . . s = t! Ass C ,a A i4 r o w.ie. o n l, ' - ' is r at t a 4 6. ti S S 9.Jil 13.669S 2.7539 . .r s o *< t t . & s s re F o n s.oC A H I tia 'n
.i h t e, . cr. bl. 10.J 0.- St. 22.7b L- -~
sonct. Ass Ciire viio A oshtH C A l. 4 'u s l o a '
.e m i n. see. 7h9u. 15318.1 0.- 4431. 192s.41
~~~
, o. o t w c v ri.opol o a orata st.p. 25 S.) 0.- 25 I I .19 owotw n acer Ar i I t'4s t o A 0410 $ 6'l' . St. 10.2 0.- 25 13.9$
suncl4ss otr>Acoon og i as. s96 . 7 441, 147.7 25.- III. Ill.bl sio,c t. a s estas sf wa A isNI.6m ( 4 9 ' 4 (' t A 6 A = l i. : hI am t a 6 loat u .. l a st r. I ? ns , 15,1 25,- St. 15.35 t A a l l. t e'e. - utesifl.lfaat 4%)+5 N e ' i' , Jh. lb.) 0.- St. 24.lb
Table B-1. (Cont.) CDhntLL. ut TCa t.F G FDD1 g utPHwi fna t!WST GuAhTeh essig - Co*fsot OVLkALL moffum Ce tu r DLowlDA Pustd COk Pow a T I Ole Commuh!TT STuuCTuwL STuot AT OkV5TAL Elvth P o s t.h PLAhi
--------humbfa OF I m D t u t tiu n LE--------
.......Ptn 5004NL mtTLw--*--* -*--ALT mVIGHT=*-= ==*-CNR mLIGHT----*
w mtAN WahCE SID DLW TnTAL #EAN/M2 TOTAL MEAh/m2 t a n . ,= net w TagaloactA su.<a n6w tilsomourto.#4 99tn. sv. 204 40.7 0.- 102. 3u.62 som3 wee = =. n.a. i hor t jw a uitn. se. 17N. 35.7 0.- 153. 66.40 tAmILi P Af.L l Ar3t Hulpat e ALLl aest uot h SP. 357, 11.3 0.- AST. 159.43 fiwl.t w ISnP'dia tadihV a=TH'8dinat
, 'h t h . se. St. 1u 2 0- 25 13.95 m FA=llV It,if t tis a E I umip. 67 - - - -
153. 30.6 0.* 76 33.20 UU tau!LV $PHaENOdAT[DAF 25 ii.39 !. ownek usio. sP. a=Pulkona
- 25. S.i 0.-
F44tLf A=PtLISC!Dat u410 sPr. 229 45.W 25.- 102 33.20 t a .e I L v A men (Lt+Cn g na t - u=In. SPP. 25 S.1 0.- 2S. 11.39 FAmlLW A4P11Hu]Dat Helb. APP. - 464 96.# 0.- 255 122.65 Fa=3Ly soutest ou!O. 5er. 407, el.S 0.- 204 100.vu temitu n a i t i o & *. us!0 SPP. 25 S.! 0.- 25. 11.39 FamlLY CAPHIL4IDAE n%In. 6Pp. 478 Ab.7 0.- 127 5S.79 t a u r i, e cou 6 Pal g u At crg;;, uhlu. $ry. 127, 25.S 0.- 102. 44.11 *f. d> faalbf L il.Jt tune 61104E (D 204 40.7 0.- 102. 42.61 T2 palD. SP.
Fa=gty a ysl a w ass]Dat' u% B is. 69 2S. S.8 0.= 25. 11.J9 --i fa*lts =tLIfluAL __
u%IG. SP, 178 35.7 0.- lle. 79.72 famibf Pp.laoCtknaL10Ah -- uqtD. sP. 16 15.3 0.- St. 22.78 - 0* DF W L t.C A eon a Fa*lby C4lt.la=&AA]D4E veui.t s g a a t t' t h l 5 25 S.1 0.a 25 11.39 .1
'" m a j i c a t.
ta=ILY Ling =lA se. - -
-JS. 5.1 4.= 25 14.3W PtLia muTICA 2s. S.1 0.- 25 11.39 -
FamiLV PA6udibaf vaGodo= 6pp. 16 15.3 0.= St. 22.74 2, t a-Il f P I '> e ' T
- t W I D a t
~
vi%%taa sv. ISJ. J u . e. 0.- 302. 41.h4 J-
"%Iu. Sr. 25 S.n u.= 25 11.39 - ._ ;r:
tamily s a .i f a t n a t, e
~
6 8* i P A C'Ft u s DePhtS$us 76 15.3 0. St 22.79 9 9
. .s , o
. .: , u
-- .=- - c 2 I se
- 4, ,. O.
."
- 9 Q
= E. .
s
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< a e 3 1 4 9,
. . = . N.
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. O O N
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. s N H2 2 3 I4 & Q
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~ 3. P 2 @@@[fh
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, iG!)I1R!]
u o,
.a=_ e z
N o 6 L, l -- t No.. 3;
'i.
- . ~. .=
.- . - ,. =.
. o e
4 1 * == -
- t. - ,
x - - 2 2 .^ n e,e
= -
, a ,.
1 N N N C. 4 4 C 4 s- - . J : d' 2 s 2 1> - :
. - - = 4 . . .
. =w 1 . .
4 4 .a- C 3. A
- H N
- Z 2 4
.~ . .s Ts F >
- 1. 3 - 1 a.
4 1 ** * . em L . GM $ 4 A . 2 N. e - E= : . 4 3 # C 2 - . a. ** 3 1 L 2, - V
- .I 1 . . .
e w . .= p
, - ' # N
- t E
I L
.O 4 ~J 4 ~ sm.e ;.
g 'D % ag nw-A 4/ * == d v . ' I . I 11"4Y Z 1
,~ .*
- r T
- - * *. s2-w 4
S m & ? Ne 5 C Ye == - a l
~~ . s 1 : r s
- s. c ._ r _ ;
L 2 ?. W W m S 7 1 7
= 3-9
. r we ,
"m"E, D
[ " M M. g - 4
. t - . 1 i , , ) ) I & I e - -
A J
Table 13 (Cont.)
, Cu==tLL at TCau 6 rt>c v
; rinsi ouapita
,.assy - co . rus. . prenef reiu est!T T H e CH-t ILOMIDA FU.tR Cokeuw&TIGk OWEhALL CDuquh TY STRUCiuht STUOY AT Cm1STAL kIVEM Pu=LR PLA4T
--------=umsta or i m a t u t on n i.s--------
-------ete sooaRE mtita------ ---- rt welcwf---- ----cRT .t: cu f-----
N MLA4 R&hGg STQ DLg TQTgb pp,gh/p} ygTgL ptAh/M2 TABON TOTab 74968 14993.6 6799.- 24341. 7678.69 233,g 4 g yyy g, m l CD i c';,
- -9;m
_XJ r ',,-T,
'j-
. _m v'
.. I AO
.3
.__. C !+
^
. ~,3,
_l.CCO Tm
.s mM
- O e
e R N 9 1 *
- O 0 % W m 9 9 A
- O &
o y e & O m O G m O e O O O e - p 4 ? 8 T 4
- O O O 3 0 1 4 o e e e +
4 s g 3 e e
- Q C O O C O
- s =
s s O 3 u
/ wJ C *
@ P O M @
X 24
- N N 2 m ge v = N N O
- O C M m O &
A M Q O 4 S k p O O a e
- e e o e 0 4 N C O O O O
$
- A 9
N,
, n g ,M5 I,, ,p\'
u mh, %. _s ( <m,' i , ,,s1: t>b' 8 %
> r
, f, o e O o a
{ - J ' c 3 m 3 0 4 re N e o e e e e e 3 C 4
;-m;s a = G Q 3 m
a w s J z A m in 7 N c -
^1 & % 4 f N D t H w t C a 4 3 4 3 O &
e e e e e
.? O p e 4 4 2 3 3 N G C e J e A
- n = 9 N N 9 e 2
N * *
- N 4 m N N w 3 m e% w
- D t t s N m N em e m = 4 0 4 &
s 4 e a w e 4 4 4 eJ
- s e ea 4 e o e e e *e * * *
- e
- e * * *
- 9 6 *
- e m m 9
- O P = N d
@ ? PP 3 CW
#9m N#m
? 7 9 2 N N N 4 4 9 3 0 m J N e 4 - N 4 t b N O 1 N
- N ei Z t t 4 s 6 1
> t a C> e e e e 2 e e o e e e o e o e e e e . . e
> 0m 3 us e
A e N e P r 3 e ?Pm 9 **aG 2 P = ? 4
= * ~
- A
- 4 K N N = N NN P 3 f P .M W n N D N N &
- ~HJ N N N m 3 N 9 m & C e s 44 as m m m
? Y m A s J O l/', D 4 2 2 1> m O Z 9 0 9 e t 0 e i t t 9 8 1 4 4 6 6 0 9 0 9 e e a 0 2 2 O L* 4 0 0 e e e e o e e e e e e e e o e e Jo O O m 6 Cy 2 4 A e C O 4 3 3 33 0 #m OG O C C C 4 L m O C C m N #
W 2 re bm m 2 1 4 s s J1 ss lsT sTO ea 2 6 e s e P J 4 3 4 =
-J 2 1 3 m 1 9 4 4 e
2 e 7 e 9 e 4 e 3 o a Ce 4e o
) ?
e mp9me e o e 4 e e o e e e e s 4 4 5 0 C = m N m 9 *3 o momm y J O
- m -P 7 O e 4 *
- N = %
- D J O & a y m 3 9 m m m
? = n E e s
% O wm N m N m 9 3 2 1 5 5
- 13 S de S s w 0 a t e e e e o e e o e o e e o e e a e e e e i E e
- cp e & wT od N & 4 #
- N
- W # # O * = c #
n N / 9 2 G N m m f N
- N NNm @ :M *AO O &
f 4 2 %
- pm
- A = P 4
? M N 9 N =
> e M
7 Y t L = V / L s m, N ,
. -4 4
Z s e* 4 4 A s 1 1 m s %- a 4 4 s 1 A s 4 a* 4
=
Ca 4 = 2 s-4-4* 6 6 4 m
=
4 2 1
=" .
- a .
e 4 4 L e 4 I tra m
- 4 4 [ l=4 L . - aLs C
L 6 4w m, se 4 1 '. - 4 *
- = . - -
[ *= ~ - : = -- 4 4 : :
-3 4
- 2 . . M .
4 4-
- =
4 Il e 4 a 2 me ts
;- . - 4 -e =,e2 4 -*3 =: 1.
a 4 4 e -
.x r T .
w on ed - 7 w c w O e d i
- 4 m = . 4 e a w/
s im i l & 5 I 4 * . <"=1 1 4 = s4J
- 1 i 1 1 2 1 S1 4 1 4
= a0 ' . 1.
f .I Zm 1* auL.4
=# 7 4 4/ T 4 4 4 4 6 4 Le l 't ? * * /m 4 2 .
- 4.- 4 f a 4 .' 4* >4 1 - 4 2
4 w 2
=
T
- 1 4
- m 4 e L 2
e J-09 OI -
*I 4
e4 = A I J4 4 . 6m 1 4
-m12!:
- 4 eL w 6 T ; a J=L *. =. *.'* a
* : . 0 7 0 wm mJ*s 26-m O 0 Y 1 6
= * .
- 1 1
M e - J w> 7-m Tw m 2m s ! = s 0 s Jm 1 4- 4 1 _--
! ! w : w 4 4
x
- J % - > ~' a. ..
- 4 r 4 J L 2 7 2 % .? 4 4 _* - g J ' > i . T
- T
- 4 +
* * .~ 2 JT : = d 's 3 1 6 4 2, 4 E T d- d ' J - ' l g .s = * ~ C 4: 1 4 1 m : 1 4 - - - m = ~ = -
- a ; L 1 4 z r, y 4 C 1 m 2 1 7 5 5 7 1 &
1
- L 4 4 4 4 s e 4 e .
g 6 s s a s r s a 1 1 1 K E b E S / V s 4 s B m : : " = 2 : : ; / A 2 * - n
- - 4 a J = J d,4 . - 4 e p = w w > m 4 7 1 *> I I I I IL L 6 4 7 1 1 L
- f - A . 1 1 1
; e t i i I L-3-7
O G N 8 2
% 0 %
- mJ G A
- HJ M4
- A 4 Ld '
4 4 UE
- 26 m Om W C e k
e DJ
- 2 2 4 M m QM e S C t,
> "e t
O G N 4 Y
- 8 %
N HZ
! \
t[ ;3'? 8 ' ' > e
' ' A se W w
l ' iE ! l. ll. J ( f 1 , ; ,f L w _' 4J
- A 4 O H 4 H e C
- 7 4 H 4 0 N
J E > m 8 S e Omm N eNNM m e@ O zmme3 N E N &We M med*>m 4 3N Se#4 9 O G Q OW N mm ed 3 m MQ e pdm @m 4 44 W TN dCo ef f 9 O A d a f S O C 0 t e e e e e e e e o e e e o e e o e o e e o e o e e e e a e e e e e e e e e a et o *N a es@ ps m SOS NON s= @ N@ 9m@ 2N 4*cNN amp ar*1 S B W de m NT N D *NN mwOfS W Nfm Wm3mT O S 3 9N NN 2 0 0 W m 9 M M 9e m Na We m 9 3 N w t o Em WM e e e e m da e e o e e o e o e o e e e e e e e e e e e o e e e e e e e e o e e C =as 4 x Ne@ mece@ s Nm a emmme e N# eM a emeetN9 app Nema C kJ O WNN @NNNm 4 Wem WeceO N QM N Ne MN 40mNN M NN Omfe
. 4 4 CJ m N 3e @ @ erm*N m m mm9 NN mN m E M naW em a 4 CA 3 4 '*
2 1> M O F 6 2 3 074 9 0 0 0 9 0 0 t 8 8 0 0 4 8 e t 0 0 9 8 0 8 0 O S 9 0 9 0 9 9 0 8 8 9 9 6 m eCu aWa
- e e o e * * * * * *
- e e e o e o e e e o e e * * * *
- e o e e o e e e 4 U = 003 eOOOO O MOO meOOO O CO COO COe3OOO 03c Occo
%> > 1 N N mm N M4 2 4 ba m 40* Ca saan a 1 00 & a J2 1 4 0 J > L e 3*1 me4&& M e&D emOmO 4 m e Om% &3 3*3mN DM4 NDD e A 4 4 5 0 2 e e e o e e e e e o e e e o e e o e o e e e e e o e e e e e e o e o e e e F 3 3 5 4 mmN Sem**
- efe 3* 9 Sm MNN 3mp e omm aree r e W g 6. m o NN m a me N ac,Omo N a N ,O Np m m eeNoy me m N em O X I 4 T m 4 m N N9 m em D V 03 0 9 JM 4
+U S s B e e e e e e e a e e e o e e e o e e e o e e e e o e o e e o e e e o e e e
> l M* @ OS c e .% O AN 2 O* OOC O WO C9m eP 9 OmeS O &c m SNN n e E meO emNNO e eOm N esee N ON soc Ncpmeea cam Nm c3 7 e Nm o m emm 2mN@ c N NN em mueem eA m mm o m N m m mm Nm b N m
F 2 m a
- 1 y 4 4 g m m e i M F Z V 3 @4 V m m > 2> 2 m 2 m M j C4 4 k A 4 J 3 3 22 34V W h m m C 4 m 2 7 tkm 4 4 4 1 2 0 4 Wm W4 Am m OeC 4 C & 4 4 3 Sm 4 34 0 0 13 T S 4 4
- @ 9 3 4 E D 4 m a R s $4 k" 4 WV=I JA O Imr 2 . 2O mCJCC3m4 A 4 '? H M S* 2 4 4 4 4 : Z : 2 E C =J4 C e 1 4 4J U2 4 >m / s 31 4 M 4 e 03 L**W= 4 : 1J1 Cm a e m2J02 cm * *s 1 T IM a l mJ4 4
- 7 m > 4 L f C E=142 m I4 = 41 4 C = = 2 1 L4A . O 4 M 4 1 - 4 d 74 A4 0 24 em m 4=O 7 %>4@ 2 4 0H Jat =4 0 m La e m . ME C 4 74 Jm m1 1w e!2 2J 4e0 e=m J* *J :" e J E
- 5 OM A e= 21 e f4 m
- V a J
CJC aa JW 43 11 J m = s 2 1
=Om :
s 4: DTUsJ2 Cs awAG4 % 4 4 4 4 41k 2J I4 a L 4 L t L 10 4 04 *==
=V~Vm 3 A m : 4~s ea11@ l4 Al m
/A A VAJ 2 4. 1 4 4 4 W I T E * *#47 =1 A4 14 7 a 2 T m 4 J 12 ; ; OJ
- 4 4
- 4 Lm e
4 Z x e- L 4 O2 5 i em - w e2 OT 1
;4 :
JFJ
& : . 03O UQU4 C eA=1 F e# A=
> OO 2 3 0 aMV1 2 4 4 4 m OJ% C I. *W 2=
JJO awa4 e e m k =
/ D 2 4 U 04 ma >3m ?Zm m
l
/ w
*1 m 4 *
> w 1 J-4 d4 LGJJAfk s
21JE 6 4 5 m P =4 km : m =m te V e = 4 L>2 22 4 2 m4wh Fw I 4 7 > r 4 ; TUN F > = J1 Jm : 2 = : J= R f nm d a f : J il l : ~ 53 L
=2 >* m m F J*
=
= m J OJT3 D J4 4 4 L: mJLJd; mJV6 3 d e k$%f f m m m m o e =
U M E E S T E F 3 E 1 E t 4 4 4 4 4 4 4 g 4 4 4 M. . I b 4 6 6 6 6 b e e e A E m J C 2 T y => : - em 4 ,'_ 4 ) 4 I M T E k 1 ImB i , i '. g ! uJ ,1 i
; _a J s 0
0 'N O 1 @ Go X $ % * @ 4 .J G Z O O
>J #= 4 @
W
- Z 4 I a. e 4 2 Ja 0 0
?4 ==
3 = m O B
/a wa D @
3 et 4 1.e e 8 a to N 4 0 0 d 0 he e e e 889 888 9 9 8 % 9 3 F* 4 0 % N O
> F
- 2
- I4
**6 -*
w
*e S s
'E
>=
'a 3 3
P" 3 4 2 t > == P= t= 4 ; e e 2 0 > 9 4 8 e f'9 J A Y D = *
- Op 4 A M
- 9 .e s r% == 3 % # N* W# "g 3 av 2 *= ?
- a 0 0 .,
N % 4 W O 9 m *= M 4 t 0 0 .2 ef el 9 4 "9 C 9 Q *4 4 == e e e e o e o e 7e o e e e o e e o e e e e g s A % z Z a' 80* e t *e
- 3 3 7 7N O P
.e tw =a P 1m m
=P 1
q 4 re
==
en
.e C.
re
*7 e .=
em D se 3 ye 1 me m
$ 0 e= P .4 es s
- es X 0 t /. *'*
- 8 2 N 9 4 4> e * * *
- 2= e
- e e *
- e * * * * *
- e e *
- p. -- 2 * * * *
- 9 == 7 e ==
- 9
*e e r == r / .
- m ? % en m 9 A no N em
* ? 2 2 == 4 1 4%
r OP O *% 9 C >=.,,3 : N ** W t% PNN OP N G e O '3 rw em N '9 ( S *e 4 s= or N 4 4 4 O 'a Z *= == Z i A "r >as'_* T 1 ha =0 7 8 e E O 9 9 t t 0 A ! 2 2 O** O e 3 8 0 8 0 0 t t t t t t t e e te e e e e o e e e e e e e e e e e o e e e aa Oy 7 /. A O O O O C CO O J O C 3 4 V == 0 C 3 o C OOOO C ? y= eo 2 P-e= 1 2 4 aa
= 2si sTe. :.
s e. C 2. 3 9 O m s
- P= ce == Z N
- 1 L A e * & *} 9 C PW N am m * # =9 S e 1 6 4 3 a e o e e e e a e e o e e 4 e=, e e e e e e e o e
/ 3 e 2 *
- r= = N 3 3 -- 2 6
'*4 # d'9 ""=d** m 3 r*
- 2 m
- r= r= 5 2 3 3 0 4 ==
9 9
- 3 W 'N X 0 # % ** ** **
- 9 ==
av M
== 4 N a' Y 3 e K= N e ! S 0 J- t a L 0
- 0 . . e e o e e e e e e e e e a . . e o e e e =* *=
e 7 es em 2 5 e f aim & em t f= 4 om em '% & ee C en rw =e s m e / 3
+ A O s e % 3 F :
t 2 N / ~ N PN P em e m me 9'e r1 C ft ew e 4 == w
/. 5 t'.e r= emm ee
- av m em o w e=
Emo m T y X O 6 4 e se 4 4,8 m. a _ 6 - u x . 4 i .= 4 0 4
- J e A *=
- 4 4 4 b d 4 u* 4 J s ".
. 4 =ne : A 4 /
**
- a e== * -
. A a 2 2 V 2 S. S i O 4 4
- 4
.4 4
- 5 4 e N 1 h &
e"'* 4 d
- O =* 1 J 4ee=4 4 ==
& [.
e=* b ==4 0 T T -e e a, J "* a. 1#4 4/- =4 . === == e e hE
- 8'e h b b4 h 4
*=
. rb&s3 4 e C- e
- 4
*U*
- N - a
- e
'W
) 4 t J'==-J-4 e
, ! == == ; 2'E1 L 7 /. .,
* * *4
- . J-
.e 4 =
4 4 4 a
= '. 6 A v "". I 1 .' T4 J. 5 4 2# E == #,
a = .a 4 2 4 T O+2 =e 4L/, F 4 T : _* Y 4 J
- 7 4 e 4 C J 4 11= - 4 . A*l i G . _ f i i
- k
==
- e= r ?.
S 74 1 *
- a
. L 1 1 4 I4 *
- 1. "r eJw
? 1 J4 4*
14 / 4 Y4 C *= == f
* . /. ; I 7 i F 'A - V4 A
2 .44 1 ~ JJ A 5 -=>==,=
- T ** ' 2 1 I i 7iLs 41 o 7 <" 2 2 *= 4 a-.,--
e .* e 4 4 0 4 4 4 - ~ Z Y 2 4 : **4O C J
- 3 4 J4 ='1*
r f 2 4 /. _ / .*. 6 - ** I 4
- I4 L= L . 1 == 7 m :' - 2 . '*. 4 e
'I t
O a F 2 / =4 = = = =0 *se
.= 1=
a == 3
% 4 I 24 2'
- I / -e 4 - - _ = -
r / T Z = 0m -
==
>>>0
. wL m L ; ; a. J >4
/)
4 > 4 4 = .= = C ; m. . - E *= T . , 7# **22 ' *L-.* '.*= .; ! O I
- 3 a
w i >4 0= 4JJB a4 V br /. 2 .2
.J. C - - - -
== 4
.J Fw4*4 a yJ4
/>V w.a ; J % J. T .J.
Cw a- 3 x 1 / ;
.e -- -
3 3 2 1 1
=
I 5 1 e 1 F F 1 f f 3 4.4 1 4 er 2 7 4 7 b g 4 . .,
,J G 4 4 a
4 s 4 s e s 4 s 4 a se s t. g 4 w 4 s 4 s s s : s ?L : -uK . --a1.=4. - e i s ' 2. : I a 1
~
- 1 O
~
4 44 T 2 .
- - r x
~- Q Ow
% af
* .t' C
. e a o i } l I I-B-9
1 i U. Ti. i'
,, f- ' s ,} e I , ' ' ' .\
tp1 ; ,!
' . - -y y - \V' \ ,
I S S N O I
- 2 0 % i 4 6 2
** O as 3 e* O toe.2 to 4 Z fan # O 2 4 *
- ea UE O O Os se Oz tad C a s't > .2 e A N me a 4.e Qt se N e O
% eO e O e to e e g
e o O O eN eI
- O% *
>* 2 N O 14 ** O ind O.e E s N O sel 2
esa e.1 3 4 a A 9 Da M N
> 3 O T O F 0 tw et t
- C
.2 e*
L 3 > W 9 5 4 O A O O e "4 3 N P "9 N == A
.E 9 9 O en 9 9 9 4 9 & & f9 O & D N O 9 5 e e e o e e e o e e o e e
& 8 8 O a e @ m
- rw ew @ w 3b 7 m D I t > m 4 N e o a 9 em =e se 2 0 0 1M se **
- 8 2
> S 4 2 e* to be 3* O2 4* e * *
- e
- e * *
- e
- a O se *E N 2 4 N 4 @ N o 4 e # o a=
0 ** e.2 O O m e O O N O N O te eu og att a 4 4 O el em se se sue "4 em A 2 > wzW 4 Oo >4 t.: 2 1> == 0 2 604Z OO4 8 0 8 e 9 I I 8 8 3 I e t
=*OV Z ed 2 * *
- e a e e
- e * * *
- 4 V o* O 3 O O O O O O O O O O O V> to a
>= Z24 6*
s Oa O% K 1 e se e a OO E O
.,3 2 k3 m 9
.3 0= i e e se o m & S *e e e e a e 9 4 4 it3 K e2 e e o e o e e o e o e o e E 3 3 5 4 m @ o N M rt > M M est m e m 9 en 4 8 8 a 9 % N
- 3 m N 9 ee O Y & c E V O3 8 J e-= e
*U 8 3 9 2 0 e o e e o e e e e a e a e he 0 e 9 3 4 @ w e em .o e f's se W5 0 2 m
o 3 & 7-m N o O N aan m c'e N O ee . o fee em Po (t f N s= ee em E O I l s - t 3 W em 4 O m 4 a O 2 1 4 d 4 ** 4 4 O a O 4 er == 44 'm eb T 4 4 ** O O '? w s J *e e a O 4 L em o. 3 4 4 4 *=N 4 N 4 O ** O A O me : v . 1 2 - 4 - e t e4 e lab ee O. e -OLU 4 2 "4 A. C UC 4 as 1 4 e 0 e e o O J 1 ea 104 -x* 1 e-
% 1 *= 1 *
- 1 == 1 == 1 0171**1 ;w 111 e0 e4 I 4a 4 7 1 1 e >
I1a v a O O o* #. O w#10411V 1 v) 2 # 2 4JZJ#02 O=0 m / 4 >4 2 o* O C2 O 1 I C ". ==
- 14 2 2 m O bI 4 4 e14 e-
- met 4 . 4
- e5 *U *J e E ** w 4 I O
- 4 L
- E 7 OI $ $1 O $ O $ 1 U 7 O O e** O g V 4 t-/ == ss g m. O.
. =e e.e .O m U. ; 24 e. ** 1*==
fa t= 'e; F ee > Ew E 4 >E >f>E >2
- I wE Ow s s 1 12 : w t
! " 1 O3 .J E O T UO T /.
- " ~
2 ==JOJO == J O J==O==el O e.2 ea e= O ===4O2O a's m 2 m UC U X0 2 N E 2 1 3 I T 2 a 2 e2 C 9 sZ s 4 4 s 4 4 4 4 4 4 s 4 2
..# F CO O A e Ca "a. m. a b b Om O E 3 #
M 2 O F 2 en 1 2 X A O O V. A ~k O O C O O a J4
- V. >= 4 m = g 4 O 4 I Oy
/ 'd M f f M 1 1
~
Q I- B-10
6 em M 0 W w 4 0 % 7
- a 3 2 m
* =J 6 as e 4 4 Ie M 4 L JK
\
, _ m .
2 . s ( l, , ' ..s-, 1 s
, m ' , +\ . - ,
2 _ an ,e ~,
- e ; e e >. .*
O # f 4 8 N CP 0 A > 0 % M
>= 2 e
; e ct E." 4 M
== A 4
E D* O
* .J D s e O 9 r= e
>= l C T 2 B M ?
4 0 == d A 3 > S 9
- e A 9 9 a* **
C e e
- 1 0 9 0, *P G em m 3 l l 4 &
- 9 Z w 7 6
- Z= 4>
> 03 a.
- a o & K &
a > .4 e-
- 4 4 CA w 1M *"4 A
.a OM 7 et U 4=
1 A> = 2 7
*I 4 A O?e t
.*2y J .2 e 4 = #
Lb
= 2 X4 wto *
- 3 ae
*O 4- Oa w T 1 8 w 6
& I i 1 9
.2 1 1 u 8 4 vJ. I 6 3
+ 4 A E O J e 2 2 : 9 et P 2 ~ m 2 l r **
I Z Z 4 5 N
. I I l 3 r* 9 m e a 3 3 $
2 0 e W 9 ?
# $ 2 3 e
ze ** H h on E_ -. K e T b C C L >
^
e ed aO, W V & h at
- r a
9
~ ?
? : ~
@ 2.- Y r-4 7
. K
=
4 l ( ( 4 4 f e 4 1 3 3 3 @ 0 A > 3 ) ) ) 1-B-11
Table 11 - 1 . (Cont.) CONht LL *tTCAlt G Ebut HANIN - CohThol ptFout rod 5tCC4D GUANTEk naTTom C.tw t tLuptua Pdeep CoheuMATION 6b& WALL COnduNITI SThuCIUwE STsby AT (NISTAL HIWt W PUnth FLAnT
==------mumhek fit t hO l V I Dal A L 6====*- * *
-------e' t u S u tl & P E mtTLW------ ----eE* wf!GHT==== ----CMI WEIGHT-----
[Anag N mIAN NA=GI STD LtV TOTAL '2 TUTAL *EAh/m2 VHILU4 P4FMIttkA 37.0S1 7.410 21.u16e 4.!?*3 6 H i t.uw cu t e t e. r t n A r A 0.1S3 0.033 0.0229 0.0046 FH1 Lum Pi,AffHrL9thfHtE 0.0b1 0.010 0.8019 0.0304 U%lo. SP. 70. 1S.3 0.- St. 22.7d PH 3 Lef m A SCHP L4 le IHf b --
.8410 sv. 2150 SSu.0 25.- 1444 775.w6 H PH t t.uw =t.at p f i me a --- -- --
0.w98 0.17 e - 0.JS84 0.0703 j, Ur.lu. se. 696. 137.5 0.- 280, 13).05 1 r- eHytup S I Pu = Cu t. 4 0.051 0.010 0.0025 0.0005 F4 U N I .i. SP. 25 5.1 0.- 2S. 11.19 entLum A m = t.t,1 b & - - 64.J15 12.a75 12.S363 2.507) CLASS OL I GaCM a t.T A UNIO. SP. 68W. 137.S 0.* 204 87.47 C6. A $ 6 P+ ll V C H A t'. T & t A a l t. f AdAntiLIDAr* A>AntLLA twicutaw 76 IS.) u.- 16 14.lb faming CAelitLLibab - CAPITtLLA CAPITATA SIS. 107.0 0.- 306 128.15 '-, c3 4 HtitHue&STUS tlLIFUhml$ St. 30.2 Q.= bl. 22.7d ,_ _t -y
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u%2p. sp. JJ9 (S.s O.- 1S3 63.41 tAditi C lk n A tuLIt. AE -- Inhwva ar. -
-- een. 133.2 0.- JW2. 154.31 -- - f FA=tLt t' U N I C l i, A L ,
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L. = M .3 3 M # N MM# et tw N O '9 r4 A O 8A O 79 M # M e4 M M N e= r9 N a 4 4 J J N se se at es se O as 3% ** S J
.J ?A D 4 J 3 1m me Y e 0 3 E C ?4 8 0 0 0 9 O e 4 0 0 8 8 8 8 4 0 e t B e 8 e e e e p 9 8 as % Oy a# 1 e e e o e e o e e e e o e e e e o e o e e e e o e o e e 4 W == O O Q OO3 OO O O 3 O O O '7 O O OO OOQO '3 OO 3 :
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es 4 A E e 7 o e o e o e o e o e o e e e o e o e o e e o e o e e o e A 3 3 4 4 e d # OAG A# A O d O O eM 3 3 AA AAAA A A 3
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- ut g F M e P= c c's e ce g rg o e e a as e A p ce cw me ce 1 rw rg A r= '"o O g se se rg se tw r= se ce De De se 2
3 3 5 C 4 I 4 at 4 4 > A to E
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^ h ***J A 4 'al me d 'A O 3 Y 4 4 7J e e 4Ja 2 as X 1 4 se O 2 2 D. L 4. J 3 em J O at 4 .J 4 OO E J4 O as V = >= =e at :3e. se % al== 4 aQJ =e e J == & e 4 J 4 ! 4 == J 1. U J A em JT e ** T ==V 4 e 0 / Je 4 J riO 4 J e % C 17 OJ4 4 m
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fe .e N
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4 se em
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% e= >= 1 2 %
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as 4 4 a e a e e e e e e e e e e e e o e e e e e e e 2 3 2 9 4 3 e 3 P & & .3 A 3 A 41 C D m == 3 3 ? 3 == D A 2 == m a e og -e N % a /> * % %
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m
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4 = 4 1 4 I T a.: M 4 e er == Z 'J J C. J . * *
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= e
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e- = 4 3 = a -= ; .a - - g e.e .O .S .Se .O. - .S.e . . - .e -
~ Z* >4 2 ** * - = ? m T >.*-s > F =? w F ** .? m F = ? = .* w ." - 1 = ** . * .
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*#. J .; O.* 0 .4 :
l 6 O -
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;^ Y 4 f 4 T E K 3 1 ! O Y 2 1 1 3 3 T I 1 F f g 7 Y f a X $
# .J 4 1 4 4 4 er 4 4 4 *r 4 4 I L e ei .
G a 4 e 4 e
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ed m a e A A a a E f f 1 '. 1 1 A en~ J K R ==e "" ** T ~ 2 2 O O C O
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Table lill. (Cont.) 04sm%t t L 4eTCalt 4 kl OV
.i a N I 4
- C' e i ! N It. M e et1= I t i .h 5 t 01:40 .)it a k T t G Mi t T I'im C U W F. P L48M IOa Pdet M Cis88 PilH A T lish b ot h et a l.L C..maumlTV S T h uC l u n t. S T ieu f AT CHudfal. pivt N FustM Ptahi
= = = = = = = = se is = N e a int 1 % D i v l b u a l,6 -= = = = = = =
======*ttb % 8. tl a h t. atitM-===== =====tT =>IGHT==== ====6.*I etIGHT=====
4 a E f14 h atan eda %Ct !a l b 4't b total es t a h / 8 2 Taif aL miah/m2 fanitu %Tt holmilt,at u 'e l o , se. 102. 20.4 0.= 102 4S.S% owiet intcakoon t a 4lLy P a t.i.= t i, a t P a..ii w o . seP. Th. IS.) u.= St. 22.7w tsalty e l = =o t tie w lis a t' vi%%Ata dP. 17s. SS.7 0.= 76 14.36 tantLv i a s i ee l te a t: t uos V P a %oe* Hs Ot Past S6H6 98 19.2 0.= 25 14.9S N* ov a niset SP. 24. S.l U.= 25 11.99
'e%Iu. av. ISS. 30.6 0.= St. 21.31 1 SH"UM ot M "'4I44134 -~ ' -- ~ -
Cu C a w t ut. a u Zufa St. 10.2 0.= 25 I1.9S 8 CLASS ImsrCra 0.u2S 0.00% 0.002$ 0.000$ $ o*# pe w ulettwa ea4ILr t' H t w o %u es t o a t: U 'e l ls . 59, 2%. *> . 1 0.= 2%. Bl.sv Pwrtum ECH i m.sve s. = 7 7 4 41. 8810 e.276 13.22s4 2.6448 uM10 SP. 204 40.7 0.= 127 So.62 PHILiam C H' *w o a T a C1 ass asciotarta d w l .a . sp. Jh. 5.1 0.= JS. 11.39 CLASS Ost t. l CMin it S u.760 1.752 2.1467 0.4293 t U umlu. sv. 24. S.! 0.= 25 31.89 ?g _f_. 3
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= 4 61 1f 8 # e
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Table B-1. (Cont.) C'ih n t L t. at TC At t 4 t Lis t h 6 Pf >M T $ 6#w 5 L C O 'e D G d a h T t.k 6t4514 = lil %CM a w s e eu f fism Ca ta t PLowlda F o o t ie Cases t iHe A T lesa OshkALL C0="tJ4 f f y S Tit uCi u d t sfuDI AT Cu t ST AL Hl WLH Poot u PLANT
*=======humtitW I'r IhistuIDUAL6-=======
=======pty S w U 4 k t, atiLH====.. ====e67 dEIGHT==== ====DHI wtIC.HT=====
N W r. a N h A 8666 STD Otv TOTAL miaN/m2 TOTAL pfAss/m2 Im aleh Fri r l.u w C ut t.t.h t t W A T A 0.S60 0.080 0.0000 0.0000 engi ue 6 L a r y we l.* 1 a r He 5 0.153 0.022 0.02e0 0.0044 0110 3 6> . 25. 3.6 0.= 25 v.e2 vutLum AdCHeLMI4IHf5 0519 $P. 382. $4.6 0.= 3 !2. 144.17 PngLue Nt*>withtA 0.J29 0.013 0.0407 0.005e u <. t v . SP. 43). 61.s 0.= 178 56.67 t-4 0.076 0.011 0.012) 0.0048 hI P et I L U M SlFu%CULA uulo. SP. 25. 3.6 0.= 25 9.62 w W P .i Lue CM a t. [Ot.4 A I N A 5AGtlTA SP. 25. 3.6 0.= JS. 9.62
~
PHrtan Ag=tLILA S4.062 7.72) 9.uG90 1.4013 CLASS OLI OCMatl4 deln. 69 600 12.h 0.= 280 96.bW CLAS5 PiiLif etat T A tAulLV A4/Haht;TluAt. m>Llh=A MACULA &A 25. J.6 U.= 25 9.62 _- la=lty ane%3Cottoat. adt hlDiLa CN15 f A T A 25. 3.6 0.= 25 9.62 , t a = li. W C av (16 6.L il A6 C APllti L A C4vilaTA 1846. lbA.7 0.* 313 2$4.16 utit ii=431ua t' ! L i ri sw a l s 102, 14.6 U.= 76 2m.e7 d e t. l i . A e l i,e C A L i t .6= ne l t m a n 6 -647 ww.W W.= 204 76.18 umia. 5P. )$1 Sd.v 0.= 151. 62.lu 6A*lLt C l a w a l lj L I D A >. twa4sa nu. 4S02. Jte.6 0.= IJ24 4Wo.67 6aalta t ua L II at
=&wPuisa S a . c. d l % t' A 102. 14.6 0.= St. J0.04 6 Aalt.s s.1 s C e w l a, A t.
i,L I C t.d A A*tHICAMA 204 29.1 0.= 76 30.94 6' A a l t y o= I A til u A e. (.L I C l i. u 6. he. --- St. 7.3 0.= 2S. 12.43 ta*ltv *> 31 s e l tr a r G1WYli no>vivAIPa St. 7.) 0.= 2S. 12.43 -
>&hlLt Lom aa l-E n e.I D A6. -
L d 4 M w i k t. n l 5 >P. 484 69.1 0.= J04. 65.46 ,--' tA=4Ly =abtLU=lbst ;-.-1
= & a6. Lo = A &6 Til
- sh6 AE Job. 4W.u 0.= 76 Ja.Sb .
t A
- I I. t
- A l. t ' A
- I o A t
& t li6 t ot i l A "i n i sN & 4u4 69.3 0.= 182. 140.40
** w a s.( w l . A > y C H l , Amt.wlCAAA lb, tw.y W.= SS. 40.u4 (f. d kt. s r i.t. A fisa W&la 2S. ).6 0.= JS. 9.02 6talLg *ewelaat JG7.4 44).64 9 s.e6.=.e>*ls f ail .. w l 14St. L.= .
rable 15 - 1 . ( Ciin t . ) L' a e e t. t L L a t IC al.t b F L ts y
> t lh ow T t ' oe Stro%D edabTth east. - . i t a r. 4 6 .
- m. e g l i= t e .w e i t.t + t t a a boekw Co=Pom&TBob bash &LL Co**u%ITV d I k bt i on e. 5 T uli v sf ChisfaL kitt k F (s.t w PLANT
--------hun ts e 6 s i h n t W I f au a l.h--------
------ u u a n t', wtifu------ ----atT utILHT---- ----Dkt e t l u ri f -----
r a a r e.
- me AN r a *.6 t LID l'- t v 101AL NFAM/*J TOlaL =LAN/82 e4
- 6e t. ] :i Sist ( I rat a 2S, 1.6 0.- 2S. 9.62 o.10 M. 2S. 1.6 0.- 2S. -J . 6 4 e a = t s. : e i%n t.n t ti a t' eliiva t a a (e.6+t& 25 3.0 0- 25 'd . 6 J r A
- 13 ( iiw ea t u a t i a t u n e t,o u e st. o L* :' ee ureu S ro, luJ. 14.6 0.- St. 26.u4 s ci i Li iv l.m. w ; ru< a lOJ. 14.6 U.- St. J0.04 ii r. l u , SP. JS. J.h U.= 2S. 9.tJ t am It.v v 4.e a + ve l ie s t av trive a t w i l.et t u a t. 427M. ell.1 JS.- 1)SU. 4 4 0 . t. 6 ag g elut a l a s i.ne< 1 J1wo, 11J.9 25 - pts. 10u.11 J.m v.- Js. ...J 7 a. i c li.
PA"8'dI" a ,. r . S M'* Js. 294 J'*I "** I 'J I e DS*"S LJ I van ast els 3P. Jg. 3.6 U.= 2$. w.h2 etelu. SP. 16 1u.9 0.- F6 2s.*1 t'
- ta=1Lt e n i 1.t.i t.ioc l o a t:
t T t ' h e. atitwavosa 117 18.2 u.= S 't . J4.JJ r o u t.1,oo.ec t. c.v . a 10 iv.9 0.- 16 Jh.mi 041u. SP. 25 3.t U.= 2$. S.62 6a=ILY Sahe i Linat C te. oe, 00 % + .41 127 Ib.J 4.- St. 24 2J t arwicia w. Fe. 10.9 u.- 76 Jm.e3 6A=ILa statrc gust
= 1,. U W i e l ( E m e..im d a hC H I A T A 76 10.w 4.- 76 Jm.h7 p = u a 6. 4 t i % w l i s pl%gATA 117 le.J u.- 16 2m.is vr ta ytr m a ar eF lt H I 76 10.1 u.- JS. 1 1. t,1 ,
eug4. 68r1.. tI,.bdA%(Hla St. I.J U.- St. 1W.44 il Lu.Y 0.- 76 Ju.p1 ._- Sci o.t l.t o l s sod a =i a T A le. ~ s t u e rt*.vlo ne tbicrl Isl. 11.s 0.- 127 43.4e u lu, e. . St. 7.4 G.= St. iv.JS [- tap 1Ll s il.t. i tz a t 5flLl$ %P. 2J9 32.7 0.- 204 75.99 o.lo. sv. Js. 3.m u.= 25 v.62 t A
- 1 L. i i r k i lit t 8.1() A L 1.1.s t t f. A & {.h a 4h4 69.1 0.- 4%W. 178.90 e.41 t,ius m ' H.I. if 30 &
LLass eldal.yla 3.236 0.4$9 1.70e7 0.2441
.. ae t o . *P. 25 4.6 0.- JS. 9.62 tawlty [ a w p ] [ i) A t i.a t v I r a p o t o = u . . w f u 'i l JN. 1.6 0.- JS. 'd . 6 2 6 a m I i. i s. P 1 i .e.1 L & &,
u g St t.L a P L a t. i't. A T A 4 *> d . bS.S u.= 311. IJo.Jl t a * ] i. t 4.1 o . '. I i t a e
- 6. v o . s t a .e t a l 1 % & St. 7.J u.- JS. 12.44 t t aa j t. f - f ( l t, ] . r a t
~'
4*e6 44.i. ,teselow St. 7. s (s . - $1 39.2% ~
- A d o s. L s .' t.a t e k a b t 51 J.J 0.- JS. 11.41 t a ' t 1. t l e 1.1.1 . l i . a t 1
- l L t .4 : F, 4 67 3a.2 u.- 104 s t .sn y
Table B-1. (Cont.) Cv% = t i l at trat t & LDDT Mastu - s . 3 3, c - t w s ., b y P .w ! D e -w StCUhD adawfab setifM= C o w e. t Lum l b a t' h e t a Co-Pv6aflom ostmaLL Cbeau41T1 SimotionL STLuf af CdISTat kI vi c PO tk PLa%T
--------=umeta if iholvim.ssto -------
-.-----itw s.: #shL attt>------ ----e67 ottent---- ----LWI =E1Caf-----
taso m -tan wa=ut sto Lev Totat etas/*2 TufaL atsh/=2 chin. sv. 25 3.6 0.- 23 v.62 t aalt a vist = J o at ye==a sv. 25 s.o a.- 25 9.62 va-asla-te tw!wseTea 2%. a.m 0.- 23 1.*J t a a* STAI L L a Cu'.w a u !
- a JS. S.6 0.- 25 4.02 Class Las?wjrooa 2.vGA G.4tS 3.WO44 0.2724 Jo10 $P. 25 J.e 6.- 25. 4.62 faalt aCit f CI bidat aCft.(Ima (4=at.tCoLaTa 546 e).1 c.- 2ea. 9=.04 ta=ILg aCT*v%Itat ACTt'** vJ% cts 3TdlaTLS St. 1.3 0.- St. iv.25 tangly naal=otival --
jg namigs*a SP. 76 10.9 0.- St. 20.04 1 64=1L3 CatCILat r,g Ca+co. .P. ii.. 26.s 0.- 302. 44.it Da=1Ly C a % C t. L L a > 1 b a t CagCtLLawla etT!CULaTa 25 3.b u.- 2S. 9.62 ta*1Le C o uf actLLibat aNaCn!5 PULCHtLLa 25 3.6 0.- 25 9.62
= I T e s.i s Losata 127, 3b 2 0.- 76, 2s.3) unto. 6&. 25 J.6 0.- 2S. v.62 ea"lLI = a * .! Ne ! L I[< a L a a m '.1 % t L L a SP. 2S. 3.6 0.- 25 v.*4 uhlu. kr. 2b. 6 G.= 2S, W.64 - --
FaalLI PimaalCtLLIDat aiastn=Is sv. )S7. S0.9 0.- IS). 70.Sl T o = =. .. I t t. a Ar. 16 IG.W 4.- St. 20.04 e a = t I, v v i T - 4 6 t L L t p a t'
< s ~ 10 , Sr. 25 J.6 0.- 2S. 9.t2 F a t L., = a= T Haf +nu s D Class C='8 5 T a t t a 4.vSe 0.694 1.0044 0.1441 so*Cta>% ..q=ac....
o h l .a . dre. 3110, 474.9 D.= 1757 Sv7.Je Sueciass = s t a ca.31> a C a esmot W [ ed a ct. a t a ally 1. l a a t s L I v a t unto, s&v. 25 J.6 0.- 25 9.62 tadlLv *om - Dia6TtLinas v%io, s k e' . 76 19.9 0.- St. 20.04 " owme= rs=a toace a - A J aam .. . blaomokaa-a "i l r . sv. St. 7.3 0.- 25 12.43 s u ai nw . , e .c =ni> > i n i i t .o w a
.e = l a . hv. 25. J.6 Q.= 25, w.02 ea=1 y a at i 4 avse volest e as Ll avse i a 3 dr. le. 1u.5 0.- 76 2s.m1 o- ., e w g ,v .v a v a ea-!ti a - l .m a g i . n e.
Table Bel. (Cont.)
- c. r. u u. = > r r a i t 6 toof SLCobb Ottap it h i
*e A s 3 ', - n j s t. ** A p r .t *< t P i t w T t i t.4 tili&.w A LL
*,s * [ t s t an (, ew t t be eed & ls A Ptie t 64 Clnw P6bk AT I.ia.
CosmostTT S T u tic i ow k Stony T CwisfAL NIVid Pilat H PL A r4T
--------nilmetH OF i s.ts I v 190 A L A -------
-------Pted Stell a h t $8 t i t H * - - - - - -*--wtT ulIGHT---- ----[,H1 i. t. I G H f - - - - -
pe t A N MANGt STD Utv TuTAL pik' A N / pa l tut AI.
- t A N / at 2 N
t A n tl e i A '* l t, i il'1II t 1 D A t. ilie l b , SP. 15). 21.d 0.- 76 60.94 eiw eit s A ePH I Piso A e Aa ll. ( A
- e'r L I SC i t> 1t 1747 JSt.h 0- IJ49, 448.ed vie l b, ". P e .
t44 tty a -P a t hi sc o g n at. o ra l p , SFP, 2%. 3.6 0- 2S. 9.61
> A a ll. V A > P L 1 H.110 4 6
*H l o. c' P P .
. 127 lu.J 0.- St. 19.2%
t A m 14.1 aowl oat 2%. 12.41 7 LJ d ** 1 u . M'P. t A *' l b f L on P +41 E D A L St. 7.6 0.- i 1H410 SPP. 25 1.0 0.- 25 'd . h 4 t'A*ILe L I L.J e Hdd G ( I D A p.
<*%l9 6P. 802. 34.6 U.= 10J. iv.50 i no e 6 ot C APo.in P I '. r. t d A SP. 16 10.9 0.. 25 13.h1 tAmtLe a h.* i en t v &&
23 1* 0.- 2S, 9.62 041u. S I' . Sueu rwi rw NAfANT[A C 4,4 ] o t A e. List 4 Jh. A6 0.- 2b. 9.62 14.020 3.21s9 2.0907 0.29e7 e,i v i.e es t c.il Nol t w d A T A u.19 op. IhA. J1.6 0.- Th. 30.94 0' } })
% N\
, .-. 3 m
% /
7
)
TC.)
.-d r -m
A 1 i
*/
. - '3c'O O
L k
"r, "*,
. 2 v
. m ;
h / 1 t L N TL T #. N A atA. 2 A d cs lik i uo o t. u a
,L i ms i wA g C
4 o. OT o, 5 . T e
. s j
J s
. m a
. /
Th sA i. 2 ct i
- a. a q T p L ,,
- t. A o
. Ts t . i 4,
h . T e a . e u r y
- . t o
- i. - . U s.
- i. =
i = D 9
= . T n = S 6 e = 2 v - t ni 6i y nk L .
D 3
&s
- t. 3 O
D TL t 2 i L A A t t 2 HT 1 L = b aS V aG W gf g m t H i.h b o, a. . t t . a re C ImsP 2 CT T . M uA f . T t 3t s e P - L gu t ou . n. LH , u t . T . L. t aS se.h o. m b . A. u m i t Hr un. a
. t i.
C s i u . n Ll . t ( . U . T
#e -
S - h 0 T 0 _ T I 2 N U L
" A _
= T _
O r i C T ) t n o C e ( L A w
. 0 1 5t - l*as 1 i 5
1 C a e
- o =
O l tr 1 s b a
- s. T E a nm ti A
[ T e - J aJ OUltt
I r . t \ Q f ^d\\ em f f' . ' D
, ~ \ 11 j'
;\
' 1,' , ' ;;
i 9 I ~d i Is' e '1Lj x e%
- e ; , .g e, J e=
e a e= 4
==e e
r=
\+'l ig 1 4 1 m o N i ./ - "
e e L .l ' 4 3 Om me'J a O en J .m 4
- A C
1 m .2
** 5 at 7 Z C e= 3= e De O O O >
0 9= me set e e e 0 0 4 5 8 N e I t % ee *e e= 2 r= P Z 4 Q O U e e e
== 7 3 4 5
t* s ; ee m ao 9 4= # #
>= 0 "*
- ar 4 e 1.= . e 4 e O O J nua L
.2 >
a g g al O == * ? ?/ 4
- 7 7 D P 2 % e? ? rio 3 4f S P D 4 & O 4 s eO O ** O so * ?=y 9 m
- M m & P* .7 * ***3 N & *49 e
- P * 4
= 3 e e a e o e o e e e e o e e e e e o e o e e o e o
*e e
.h I eC O -e P == ==m==** a .e .o == 'w ? ==.o % A tw aw am w #
3 e be "w .'s M se == @ d -e .e N em ao we es r% 3 4 e e -o N en om .7 Z A 9 0 W .e == s e1
- 3. I a A me C >=
> 0A J* e o e o e o e e e e e o e o e e e e o e e e e e e o e e C *e as K O .= 4 N e#*e a e # # e == 3 no e # =
- e- * *= 4 0 e # 4 *
** 1 3 # em C N N O c'e m N rw tw N P r= N rw N P O rw oNN 2 n % N '?
6 4 4 C 'al en to =e me *w me 4 ee *'m to 26- ** 2 W
-f I V. D 4 J S 1 s= == T 2 4 02 2 O "'e as 0 0 0 I O 4 9 9 3 0 0 0 9 I e B B f 8 I O I f 5 0 e e t 8
-a Cb 2 f. 2 e e o e e o e e o e e e e e e o e e e e a e e e o e e e e L 0G O 4 OOOQ d O C O O 3O OC 3o O O = C 3O O O eO 4
%- >= = 1 N en # tw e- 2 Y =8 4 *
[ e C1 eaisw s : L a 3 e
-. A kO s 8
- De T4 8 O e m 7 9 f'e m 9 A se *. * ==
- r= N == *e au 3 P= 4 7 -e "a **
- c'===
s & A g 9 2 e e e e e e e e o e e e e e e e e e e e a e e e e e e E 2 3 4 at 3 3 e 3 OO 34 == e A 3 4 74 OeeO # # a- 3 e .1 e a O-E == ar 2 6 . * *t o as==**e A an ==
- ee == A ==e a e 4 -e v e C T 2 4 1 **
W 7 0 9
; e= 8 s J $
0 s 2 9 e e e e e e e e e e o e e o e o e e e e e e e e
>= 9 3 *s % P 9'e we 9 & em eo # *w e 4e se .o es ds .o O CD 2 r4= A L
- 4 W ** m 8 2 #
me se N C en O m se N O g r"e N O
-e N m e=
.e A N rw e 3 rw se Er # ""o den 4 N e's "1 P=
%0* O 6.e
?
1 2 L'" me og
# Z /
M2 4 me a L "J 3 == == == e 2 E W T = / C2 4 s ; 1 at
- O W s -e == . - .
**a=* 4 4 4 2 4 4 2 T 4 1= 3 W at 3 = *a. 2 .1 ? / a
- at i- == 4 2 4 >= == J 4 =E aJ 1 0/ Ja 1 4 4 *e t & 7*.
3 *e W 4 C '; Vb w4 4 =16- J 7 Ca T + f 2 * *= : 4
=1 *e 4 =4 as 1 C *= 4 2 I O 1 s J4 1 4 JJ 1 == 04 *
- V. J4 '
# 4 J C 4 O! 0 == ma e 4 2 J Z 4 i -
- a J V O #, C e-e 2 2 e L == = b 17 6 44 L at/
4 - 6 -e m ? J == 4 1 - i 4 1 4 - - =
< Z 4 4 6= 2 *= a 1 L ; /. : 4 : k3 =s Ym ; J == - ==m E % r= 1 / 2 4 ~ z J . .
..s1 1 s2 I s : 4 C w e at e e e er me 4 4 -e e at 16 at 4 C g ; 4 ; 4 - ./o e g ? p 7 .,i.e - .*- . -
v 2 L ct 4:--J4 ' sxzu - - r J
- f. 2 ? 4 4 /. s 1 .3 14 1 1 1I
>= at 2 4 J *2J* X: sI /-74 04
- f. . - OZs.4 J: J s :
*= . L 3 *Z s /T:==2:- 2 1J2 s.4 s 4 4 : - x - .. -
- s =* % 4 3 L-6 JB I- T I == 4 4 e '*. 3 a= 4 C ! * . I as 4 2 4 - W V e I L 6- E I *6w'* m- '.;
- E E4 -= me e ! I C 1- 1 * - * *a e 4 4 1 0 *e47OL == 4. = C 1 V V == J !E Cm - . 1 2 a =L =L =,= 74 e- - ? 7 I .0 =e AT== are; m - 1 J =4 x=- ; - "
-at -4 T - 6a = La_ Jm'_ r4
-e 4 s
-:" Y UF s
F F 2 == 7 4>e s m I> p : > ;2 > p w ya 1 2 g at
-e
.J J .J J ;- m*.J.a= at J4 > 1w 2 w 4 s ". !
2* I T 3 # I s O 2 4: ! JbTT. es f - JJ?
- J A J. 4 *.J.'.J +
,".O L 2 at 4 4 C a == = e = .J. .= . - - -
% K I 7 1 1 3 1 E E 2 3 1 . 3 4 4 4 4 4 4 4 af at 4 4 4 4 4 at d & T 3 E f. /a is A i e a a e + a a e *
- e 2 0 2 O C 2 # /
~
. -k : ; J Je 4 ** / = e a- >= 4 es C er I ; T L L
'e
*. E w a "
s a T"* ' L b"o
Table 1[1. (Cont.) r-Luhht Lt. at TC a t.t & FDOV HANf4 - CD s.T w ill ht PliW T t ud THIkD G04kTth MNTfum C uw t' DLuhluA P0ath cod PalH ATION OWhSALL CnamuMITI STHuCrudt study AT CMVSTAL H[VtM POetk PLANT
--------no seu or innivinunt.s--------
-------Pfa sounPr atitu------ ---- rf uticaT---- ----car .ticHT-----
ramos a ataN HAhCL STD De W TOTAL mFAN/M2 TOTAL m1Ah/m2 [ SAetLLs "ICNOPTHAI,Ma 25 S.1 0.- 25 11.39 taglLY SEMPOLIDat' H410 SP. 2S. S.I 0.- 25 II.39 t441Lf SPloNipat P 4w & Pw irl ooSPIO PINNATA bli. 322.2 0.- 407 175.67 PMan%oSetu HFTLkOHWANCHIA 76 1$.3 0.= St. 22.7W SCO L61.t. P t 5 50useATA 25 S.I 0.= 25. 11.39 siste. SP. 102. 40.4 0.- St. 28.31 tomtLV %VLLip4F t44Gadt visPaw 76 15.3 0.- 16 34.th SYLLIS SP. 535. 107.0 0.= 280 188.62 }d 6A41bV Ft htHt LL i bat. og uNlu. SP. 25 S.1 0.- 25. 18.39 1 ta PH Y t.um mof,Lusca CLA%S AMPHI.tuhn 0.102 0.020 0.0413 0.00u? l 4 # 11. V AC44THOCHITh%ID4E ACA97HOCHituh4 PVGMAEA 25. S.1 0.- 2b. 11.19 t4MILY 15CHNoCHITONIDAE isCHNOCHtfDN PAPILLO5us 25. 5.1 0.- 25. 11.39 Cl a ss HevALvtA 11.306 2.268 7.9011 3.5003 Latvtramptua pournut 2$. S.1 0.- 25. 18.39 FAMILY CANDITIDat C A m b i l A u t.H A 61,OdlDAhA- bl. Ik.2 Q.- 25. 13.9S . . - - - fAnILV *VTILIDAF ' ~~[~ ~i q Iscwaolo= wtCowvum 25 S.I 0.- 2$. 11.59 ,- 3 S.8 anscut us t.a r t w at,t n 2$. 0.= 2%. Bl.39 t A m i l, V siSINelDAr Cwasso3rn a vINCINIC4 121, 25.S 0.- 121 56.94 $. tagioe i t'L1,1 = I o n e - ,- itLLINA SP. 76. 15.3 0.- 25 13.95 , - Cl a ss Gas twoe ina 23.190 4.640 16.6056 3.3218 ta=ILV AritoCINIbat ACTtoCiva r a m a t.g Cut A r a 102, 2o.4 0.- St. 21,31 Fangtf nuttiriar autLA htwIATA 102. 29.4 0.- 76 33.20 - F4*llV CatCloAt CAtru= SP. $1. 10.2 0.- St. 22.7h ' F A M I I, V C6et p l[ HLI D AE rktPtonta matutoh4 lib. 34.1 0.- 102 42.61 Ert r . CwtPlenta plana 25 S.l 0.- 2$. 11.39 , ; 6 A=It V CP N I Iw i lt*46 ;~-;I_'I
< - N i f et t u a t.u'hNtH4 St. 1o.2 0.- St. 22.19 p' t- ;) _,
C*HITMIo* =0 'awog 102. 20.4 0.- St. 21.31 h{hh3 p Am t e.V roi e =,6 i.s an6 y
= i r s I i, a i< .. 76, 12.2 0.- St. J7 3 tavil 4 = A w G l '. t :
- u. l a t it. A ' s '. A AP I( ' 127 JS b at . Ja.19
- ,, t .. t l.i . a n ow s oC l esc T A 2S, S.1 0.- 25 11.39 w a wi; s o
- Li.a i A W All.t t A N A 2S. S.I 0.- 2%. 11.59 O O @
., .s., .T Q-W-.l ,
)
' ,a
' i 9
9 N 0 1 a e % C e J 9 A M e .J se 4 @ 2 4 I e d 4 X JE e 3 as ** ** t' D 3 .h 1 av 2
== 3 at #
I C. H 4 en e O m a>
- 9
- 9
- 1 O N 8 E e s N D 2 P I4 W O4
- me a e m
3
>=
*J B 4 *e 9 O* 4
>= 4 O y g p e et 3 m
.3 "
1 3 D s m a 5 8 4 0 0 4.2 D
"9 7
7 m W O 7 .e= s e'= J 7 z r= 3 3 or 7
==
.e 9 P*
7
- m
.e
**
- e7 3 7 O t t e e e e e e e e e o e e e e o e e e e e e o w
ch 9 e3 9 9 **
== .=
.* ee
.e a
N M
** ==
N et N n r= N N f*e m3 3 4 7
# .ee
.e 1
c's 4 e ee r1 N
.e N .=* * == ==
.e 2 0 0 4 % e m 4 2
> t =
> ; We 2 a
90 >* a ., e e e e e e e e e o e . e o e e o e e e e c -e 4 i e e o - e o == == .e 4 e ce e .= .e e .ie e e e c C he 3 3 N m ce o N r* O d # c & M 4 o Jt # m o C m N rw as er 4 2. 4 .= d a4
& >" E'8 1 4 : A > 4 L^ep 2 a D* == 1 ?
4 0 3 1 O J4 9 9 8 0 0 0 8 5 0 9 9 0 O S O O 8 0 9 9 aa OV E e o e o e e e e o e e t. I. e e o e e e 4 V = /. 2 O G 2 O Q O G 3 O O o o == G O G O 3 @ O O O V >* De 3 en e= .2 1 at ta *
.a. O .L as : -
s> e
- S X 0
., = 0 1 3.e e E 9 == .= = N N =
- N
- N p e o e N .- 1 e N .=
.il 4 #1 S 0 2 e e o e o e e e o e o e o e e e e o e e e e f B 6 4 # D e 3 O c o 3 e .o 3 2 O b 3 3 ? A 7 == 4 e e 's == ee P.
. ee 3o N -e N e 3 N. % no N 3-3 .1 0 % e% .o s O 3 6 a.1 - 4 4 V l
) I 2 0 e e e e e e o e e e e , e e e o e a e e e o M l e r e .e == A e == ee == m 4 N c m .e r .= N A = #
A 9 2 N N N o O P= M d O O N O O 4 3 e N # "'s N f N
== .e 4 o si e .=
2= .m e 9'e 7 I L.e 4 1 4 e.- F. 2
- 4 i a m 4
- s. i 4 . 4 . i 4 y A 's *E ==4 7 .O e g
- 4 4 ;
- 4 e, e ag 7 a 4 [ 4 1 ao 4 C ,5 m n 1 O .= =4 1 4 1 " e V e I'8 d e's 4g gg e es e * [ y ;
** .2. ; . 4 2 *E _a. 4 - I i ; 4 Y.- :- : _ x f- a,' =. =e =_ . --.
- 14. 4 _2. - v: 2 4 4 -
_ - 2 4 14 t., 2= -_ - a.2 La e. X O e= 4 2 .0 4 a e se 4 4-a s= 1 1 -C - .; : e s -- s 4 - e .; e r ; e : e r 1 4a - 4 4 4 *; [ 7 4 _ e. _ 4 ** 4I-W 4 '.J .1 3w 2 e e3
- A u a e OJ1m L h21 - 1a1 4 e s( e 3 e4 a.s . 1 -
$ 8 D 4 3
- I . 48 4 1b4 -- .h E b 8'" 1 1 me** 1 mi h g 1
- 14 1 ** 1 ^ * .l _ 4 1 *"
.,$ 's*
me 4 2 w re 6-= : 'a, Y f.
's -
4 L: -*e402 / to.' 't; ~ 14 1 2 &%V 7% 41 V. L / %
.h A1/ -e
'a' 4 1 r ,. .' .' L .0 t. . == L M ~ 4
! =7
- J I .
; ', == A h- 7 D T Z 4 a
.a - 3 e4 4 e 1 e et
- me e1 4 eT4
== 3 e4 3
e 4 e 4 2 4 m r ev =;
- e e 4
=
1 4 e 4 ', '." =f
- e =
E .) 2 1
- E d E .h E e. $s 1 ) E e. '
I r e ==
= s
.-e e .; .J.= E .- 4 2 ?, - - - -- I - - -.e -e -e - - .m= Le s [
. a- > . no J>w De a n= 7 F & _J - 2 n= E >? = 2 4 > ? > X >= t am ? n. t w p a * == 1 m J ; m =*e =
e EI MI e I 1 e$ 8'" 1 [ T /. OI e* w I 7 Ir 2 I w 2 .E 1 E ~. > -e _
, ,,., - -e .E= -. 4 *.E
_ f, / r 3 .d d. *. .M C
. e.d I - 7 .E .E.e E. .m e .e . $. e
. em
".# f W 7 7 4 4 1 Y W I E 2 5 2 9 3 3 7 3 9 9 1 3
- 1 4 4 4 4 4 J L 4 4 4 4 6 4 4 4 4 4 as 4 4 4 4 4 4 4 I e 4 A e 1~ / ., Vi. l S e 4 .6 C. 4 a a 4 a & 4 'a e 1e e *
, 2 0 ? / L 1 -1 1 2 2
~~
**> 44 : : :
- C :
/ > 4 e r /
er "* 4 7 ;.,, L L a= a I I k k = , , h l l l I I l-d-25
e m e
=-
=
= 2
=m i
= / 0 1
= h ltfl L. Ta 6 na HE 9 a b GW 8
i t l tt. v t i e 0 t . m 1l i ka 0 N 0T 9 T = O 0
=T 0
=
= 9
= 2
=m
=/ 9 -
7h 9 Ha 6 Gt I s S E m f t L
= A S
= T 3 T = U 4 N = T A = 0 L 2 E
w W
= = L e 9 S W4 J
- t. 9 0
= = L
== l. 3 S. %.. l e.
S3l 5 4 P = = D 2 8
= = 7 2 1 41f4 6 t
e = = $ t = p n = L
=i 6T f
h LL . . . . . . . 1,f t a
- t 5 25S2 )
S 9 0 f t 16 S 2 0220 1 aa Dt 3 1 I s e f 1 h e 4 6 I s W aJ u *, t 5, uN t omk ira = == t t t r a h $H . =. . . = . =. =. a C t 0 0 60Q0 0 CT f u T w Ma f t i o6 d p
>=
P ieru t 4 =
=
Lp 6 u*t t = r= ) w L t as t a = h . 1 42.I. 0 . e D u=a S S 00S0 Q n l t m= t I 21 3 % u p p = m ( i
- t. u =
L l =
& C >
=
t = M = . . . . . . . T = 6 5 tt5) S S = h 7 2 oS2b S l l 2 T T I IN e m - li C - S s - u s i C S 1 S h t t w ) t Pa t a t m a a l' a t t
. i t t t s .
n a .t snSt P iuT$ i a T o l vewl l e a C la v. t 6 mrtt . a . ( . r1 mu r st kPP H ee csoa= S t 6 t a u a P n wis n i. wr e aa'M. raa y pPi s i tu.
% u
- i. l. p 1 i m t i .ay t
=, v oTl Ut f = !a=I - om l p t a L 't mNi
- Cu B C o r
l l l P f a u u a a a e = g e f 7 = l
= >
J p a b 9 l f 4 l f a sf a ) a d T nse t [ P 73t 3 rJ@
, .j ,i i-
-( ,)
-s ts ,
II' t;_ t > 0 t N O 9 3 e Z 0 % 43 as .J t 2 m
>= J s.e 4 e 2 4 1 @
4 3 'J m K O. == 2
- m 2
- . e >J "e a= 2 as N 1 C t* **'
> 0 C e t he P B
- 1 0
0 m
- 9 3 e t % N be 2 e Z 9 si
') m N M E E
a== N a a & 5 4 N 0 == e Da 0 0 4 2 0 >* N 4 e oo
.J I D
= 0 0 + 7 e e ea m
; 9 0 e 1 0 0 1 M 9 0 te D 2 6 9 A e m 0 A a 6 m I ** d >*
= ;2 4 e Y 4 h h
& W .3 3
- 4. 4 4 0 'c"s 2 h me 3 3 m J '* # D e .,7
> == 7 F e .7 a1 J O C' 4 9 2 /2 e
- e. .J , a= p s
QH % A >
>* 2 1 4 & N
- : o no s1m>
3 s 0 3 0 Jm & 1;: 3 w Ea.6 t *e 4 4 M S e s a
--a. S O t 4 4 2 == A 2 e e c Z R 0 2 N i) : : 0 %
J> t a 's t
)
0 2 6 e H t a. M t E D m
> ee te se
=e E J B e 3 >
b e A e e.= M 9 w
- 1 e
g ! -I sg
- w -
W t
\
" e
" i O e
_ e., ; a ,,
- r~ .
4
- 4
.*
- L .,.
4 *
. e p } } o T-5-27
Table B-1. (Cont.)
., CUhht LL a t TC a t.t 6 tbDY masig - u t sCuaws;t hePuGT fnw THgpD Cuamite muTTom Cowt PLuh!Da P0ete COwrOraflub O.he&LL
- Cd=MUNITV STNUCTurt STUDV AT CNYSTab PtV!N POef h PLANT
---- ---mumbtG Of thDlWIDual6-=======
-------p6w SquaHL meYte------ = = -- e t i mEIGHT==== ----LNV =EICMT-----
Tasow a mLab ha4Gt STD btv total pla4/m2 TOTAL mfah/m2 FHYLua Pt. A T Y Ht L* t = Tnt s 2.037 0.291 0.3S34 0.0502 HNto. AP. 151 24.6 0.- 127 47.4m i nit um A SCHE l.r ! %1 >t S 0 0.0 0.- O. 0.00 untu. Sr. 204, 29.8 0.- 204 77.90 v H y t.u = heathTINta 0. u.u 0.- O. 0.00 unto. .s P . St. 3.3 0.- St. 19.2% r-FHvlum a u k t Lilia 20.#00 4.126 6.7609 0.96S8 y u=Iu. sp. - - - - - - -
- 25. 4.6 0.- 25, 9.62 wn class Ot t G0 Chat T a a ustu. $P. 240 40.0 0.- 127 49.44 f4 C t.a s s FottCHat Ya 00 tantL1 AwantLLIvat omtD. $P. 2S. 1.6 0.- 25 9.62 tamlLf CaellenLloat CaPITtLLa caPITATa 600. 94.2 0.- 142. 145.12 HeitWomaSTJS t!LitDR415 4W4 69.5 0.- 280 101.56
**DloaasTus cat.IFowhitm638 6e#, 96.2 0.- 438 ins.Il il N I O. se. 153 28.W 0.- 76 27.22 e A=II y C l - w a i u t t p a t.
THa=fa 6F. 4602 214.6 G.= Seh. J46.JW FA4]Lt tuh1CIDaC
.auPet sa sa Lui,t a St. 7.3 0.- 25 12.43 CZi_;_,; ;
Fa4ILV CLYCtbIDak GL(Ctwa amtNICANa 102. 14.6 0.- St. 20.04 ( ._-l '_M F a u ll.T Ga%!ahjbal - 4.L t C t h o t. be. - -- - 2 6 4.6 0.- 25. W.62 i_- HtSIG= loa 6 - ^; t a
- I I. y otPTis n*>tIPalPA 2e0 40.0 0.- 16 24.t5 g . _,'
f a 416 3 obanal=*a.laat t , u = * = g r. t > t s s v . 2St. 30.4 0.- 102, 41.21 ,--
'- 6 ta=gtt m aut t.os t n a t ,
=&*J'm a 96TTIMJ=tah 609 7J.b 0.- 26W. 146.4% 77 t a a ll.Y Pt b e inat , ,
- t.at q%t Nt t s CuLwEu t 16SS. 210.S 0.- 689 249.14 r_. -
=>>>Is Fal.6a 64, 7.4 0.= St. 19.2%
o -t is sorCl%ta 2S, 3.e 0.- 2$. 9.62 t: u r. t o . SP. IS). 21.e 0.- 102 40.07 .;_. taalty ohupatual --- nineaTha CuPWt_A 16 10.9 0- 25 13.61 t'__~
' L- -
t am t i,y okHIhllDat _ w a PI O % Cobovl.O.% daa*s4Tus 2S. 3.6 0.- 24 9.62 t -I M al.s.Pl a d F-la k a 76 30.9 U.= 25 13.6% [72 6 s = 11 g Pawanelvat au n c a.2..a p-ILwsmat IJe). Jb4.6 0.= 178J. 673.73 t a = 11 y I.u w s t s, w t I t.a t to=adt *. t a l s :.v . 25 5.6 0.- . v.62
bil)) L' Ib } . (C(>ill . ) Cla%%e LI **TCALD L 6 l'It V
, T H 16. h G o s w i t te n a :, t h - o ! M .4 = w i . e b r Pibw i tilw t i.ow ine A to t w Cow etip A T it.h ov6saLL nsTTO* C ow r.
Cu*misNitt STwortunt si t' D I AT Cwys!AL htWtk l'O u t t' F L a *i r
---- ---husetW nt thblWIDUAL6-*------
-------pt> SuuS>t ptTtH------ ----etT m t 1 ( 't i---- ----OWY =6ICHT-----
b A v. c t. sib btW T O T a l, atAN/a4 TOTAL ktAh/m2 taup N etAN P et i1. H e 4 w T u it i ll'i a D a 14.S40 2.017 I.20h5 0.4S16 (t43% Cwdir At t a pinct. A s s Cite t Pain A
.* D e w (aLasuion JS. ).6 0.- JS. 9.e4 us t it, vv .
saintt A n usIwaCioA 204, 72.67 u .4 t h . svP. 560 eu.0 0.- su e.cL a s s =an4CostwaCA 16p i 6 w Id.IPiniA m ( A a i t,y a . r eto k 1 n 8 t' I u g i 6e. SP. 2S. ).e 0.- 2S. 9.64 W tA=ILY t 0u 16.10 t r. St. 1.) 0.- 25, 12.41 gb dsto. Sv. e oweit ie a *Pu l eein A tAalbf 188 e* t.L I SC l l' a t, 16 10.9 0.- St. 20.04 ONtu. S e' P . tamlL1 & *ta l i nu t b Af elS. 18 t, . 4 0.- 382. IJ9.17 H N t il . S P t' .
>awILy ainn !! at tag lie. NEP. 22w. 12.1 0.- 127 43.40 __
tA*]Lv .t s i t l o A t ut.tu. NvF. 25 J.6 u.= h. v.62 t a is l t,v a t t. I l lba E ' S/. 429 11.1 0.- 159. S6.4u t.Niu. owi e w ..e r A pi ava t a m t o.: A t P e.6 I n A t a g r ee t u s 81 m = a +. u t 25. J.6 0.- 22 9.62 t a = 1 t. V C a t.s. t A % 4 s s 10 A t o% t ie. AP. b1. i.4 0.- St. !w.J% t' a m 1 L y n g o veit.) f IP A e St. 7.3 0.* 25 12.44 H i k vL V It vleuwACANTHA
> A i.1 t, y y 44,0,e g g,4 6 r a .uwo s se p. 127 Am.J 0.= 117 4*.31 e a m t i, e etsapgua, etma*Hs he.
n 2b. e.6 0= JS. s.t J 6 & a ( 6.1 e I N r U T +4 w il A t: 102, 14.n 0.- St. 20.04 vih'41tA Sv. is. 3.4 0.= 25 W.tJ o a. t .o . F. e* , t a m l 1.1 t a .. l H I p 4 e ar + am ert tenahA 2%. ).h 0.- JS. 9.04 7.3 0.- JS. LJ.43 _ ._ n iwlu. hr. bl. _ sutouttw haIAerla C ap got a zne a 2$. 3.6 0.- JS. v.62 hp. 25 J.6 0.* 25 9.64
** % I ia .
s o n. 46. t > > w 6.e r T a s i I A 8- a f u r o s. a , Ine A 25 l.b 0.- 2S. 'v . t J 28.21S 4.011 0.1 16 f* 1.1E23 r.e p t .n m e r n t ..s o.. w s a t t omti no. JJv. 32.7 0.- 127 Su.11
% o, 8
f%
'f,,,
(' , ry' \ i s ' e l i ' t W O O ce 9 3 5 6 % e es .J b 3 ea > .2 m
& . I e #
as 4 O3 8 2 4 *= rt (* > d G s O
.a== 2 .a A 1 G e= *A
> 0 O e eH se e e 1 9 o re 9
9 re G S 9 %
- re De D Z .a
- O eel e me 5 9 W
S te eo a. 9 9 De M 4* OO M 9 De e
.# 9 C
.J m 1
.XA B 9 d e em .m a m % eg 4eapNO es 3 m m P4
- m N* mO4 7 ee se N # m e 9 0 a e *
- ee #
- 4 e a C 0 == 4
- 4 0 e e d* e e3 7e* 7 e e e N e
*: 0 9 e e e e e e e e o e e e e e e e o e e e e e e o e e e a e e e e
% 6 4 3 e .= N w e APP 3cP#e* 9 o D @ @A *e eo se s D de ? * ? 7 D 0 0 *a o@ .= ce a m e ce 3 @ 9
- N re mM3 e se -
2 0 t A c- == se e m d B 4 ==
.T== to >
- 3a e * *
- e e e a e o e e e e e e
=e a. .,a owe e 4++ + o e
a o e em 4 e e * *
- e e ro e e
+ ee +
e e
- a. T #i a m e es c. ce m m.* .= e n r ee s m re m ma r* rw e em o.eet g
a m rg eg e
.ed t.o J. Q. P= 9 m 9 e #me O N o.e 4 em A> me A 4 N we J D . *T 2 Osm M. *= T
. : 1 3 C r1.2 4 5 B 4 4 0 $ $ 9 0 4 4 9 0 0 9 0 8 6 6 0 8 8 0 8 9 0 8 a
.J 6 : Q 34a e e e e o e e e e e e e
- 0e e e o e e e o e e e e e e 0
o e e 8 e e U ** *** e C O o ooo oooooo o o o o 1o o oo oo3 e o o C O O u >= p= 2 em ee Da X X. 64 se e & an 4 5 ms 0
.A B OO 1 0
;A k3 e 9 J ** L 8 *P*mO Pe 4 4 .* Am34M e O e e e .* 4 ee N e se N e @ d
- 4
. US S I 2 e e e e
--,e e o o e
.,-.o e ee e eo e e
.,e# .e .e .,e .e .ee ,e m, .e ,e ,e, ,,o ,e
, 2. a 2 .
. . o - ,2 - eo oo.
o --
.o ,s.
e .e . . 3
.e -
- : = . e m -
v : 2 - a~ s
. LJ G a .
M
$ 3 o-e e
-,.,e e
m re
,. m.,-. .o .o ,. - o.
re ce m n m om mo e .
-Ne o e m
e
>=
e o m e e
,4- m o M.e m N.e e,o- o. ,e m m m.e .e .a .
N
.m - i t
~
j e . O. i i I 9
= t
=
v .
*e l Z 4 O 4 1 9.= .a .
, .. a g Ee f 8 : W
.M .e .m 2 u , .a
- .. o. '
- , .n o a
^ e ws:
.aa a
a . w : . - - a-coo,
.. l os
., s.a a.
-F et., a e.
=
.a o.
# e, 2s.
a: a a e- 1 e g 3.=- e/ C me e er s T 4 en . C. mm 2 1: == *. 2 / p 1 - 1 - 1 s .'a c2- e - a v .o .= .. J a # Ja /. :- _2 : r . aw ma e - o , ., 2 - o o. sa,e ..c o, . =. _c .,: e .o. 2 0 e m : a , - m :. _- u. azes
- e. :
. . v u: s.r...,sa.o
. , 4 . . . . ,. ..-.
u o ser-s
. <& s 2 - m .c. : ., .ss
- n. .t.
s a e
-ma
- 9. a ~ -ao - e , = .=. = a= aa,<-.as, . = e : - ..-2 2
. O O .5 : ..o ., O- 1 1 C C m a.u A I s e rT E : . : . = : .= I s--
uco.,: = = .sc.
- a. .-k .4-aw: a Y
- a. .
,** . a .a2:c,.e. 2 :
- 1 V. .,Y
.z?a . .. 1 : u.: v .J .a: -r .3,e 2 =.
e 1->:, e u ee
.,-1.,.
- 4 a-:
- 2v 1, --
a . a . a. , -
.a. . a ,. .e a u. 2 2-
.s , . a.:
- e g
i V
- .a..=.=.32 : a. v a r .a. s s s e : 3-
- ao :
. z -
E uu. -.3
. a. . u..a u2_ a_ v v a . -a: .a.
3 3 3 3 3 3 e ara a-
. .N .f .F . .E . .F .E .#
. a - * * . a . e . . . . . . .
.J f G F : V
- <~ . .a a M . : . TU Q
~3 L L o. A H
I-B-30
q .
\
t t tw a 4 X @ K E % =e a O R O m a, e e e 2 4 . ? 8 4 w'
- D .o n 2 m O a C
- n 1
** A 4 **
Z : 9* 4 H e 0 e e te m 5 M e 6 8 m ee 0 1 N O% CP
>g e T 4 W G+ **
=8 e
s
>= *e e a e9 B 4 9 P e H i : 9 2 e f.e o 4 0 *e 3
.h 3 >
e D 9
- S e e e O .N O 4 i e a 6 4 0 9 9
e t e. 2 0 0 #
- w 5 2 rw A 9 a 2 == 4m aa e
- C3 1 = 4 E O L >= 4 3 ==
s 4 4 : s 9 I b == 1m M 4 : f 3e 4 ',: 1 %> ee OZ a L4 1 1 24 8 as : % 2 A2 e e y e= 4 L 8= >= 1 e
> 1 1 4 's s 5 b
ami : a= 6 i 2: 1 t 4 e1 AO ==
- I 1 8 *=
.J 4 4 f s e r o 2 3 2 0 4 m 4 = m & 9 a 9 C 1 & 4 E **
J C3 9 9
.h** 8 ew I
; e 1 4 e
> 0 0 A 8 2 =
0 m P e= "4 ee F C 4
- e X a-C O L *
^
e
=
Am d b*
' s *** 1 .l, v. .
M { L b 9
- 3 e
- . C r C -* 2
/ > e
"- 4 2 4 h
. E J J ) )
1 D .
Table B-1. (Cont.) Cl a m h t. L L mk Tr al.t 6 tDDI H&PohT top SOURTH winkTtk nasim . CONTaul O t t k A Lt-Hi tT T,7 m Calm t PLhalD& Pilet h Cs'R F0H 4T IDh C04m09177 STwurfunt: 37ung af Chv3taL WIvt p POutu 6L4m7
....--..mumHth DF INDIVIDU485-.-==*== wp.lGHT-....
. . . . . . P t se 3.p n g a t atytw ....- ....wey at10HT.... ....pmT N m e ah W a h l, t STD t>t v TOTAL ptAh/m2 TuYaL miaN/m2 T & X O's 11.351 2.271 1.494u 0.2960 PHILuu Puk If t.p A UNID. $P. 2334 422.7 0.- 1910 831.09 PHYiU4 ASCHVLulNTHtS IS). 30.6 0.- 76 4t.e4 UNID. 5P.
0.153 0.031 0.0521 0.0025 PHILum nFmfaTINEA 61.33 UNID. SP. 331. 66.2 0- IS). e.
- A N ft C009t DNWow Im DATA l. I N F u l T*t SP Cone 40 42.628 9.526 10.0Sa6 2.0117 s PHILUm AhhtLIDA - - --
i CLASS ol,IGoCMatTA - - - - - - W u 'e l u . S P . 1095 219.0 St.. 431 165.42 CLA5S POLYCHAFTa -- - - - - - - - - f aull f AM A"t LLlD AP-- ta SCH I 5 fiin t W I NGil5 NUDOLPHI 76 15.3 0.. St. 22.74 FAulLY CAPITtLLIDAt 22.1d - C A P i t t la t,a c a P I T A T A - -- -- -St.- - 10.2 6.- St. at:D104 A5TuS C Alit 0RMIENSIS 127 25.5 0.. 16, 31.59 uMIu. SP. 255. S0.9 0.- 127 50.93 f a n t t. V ClkwalublDAE - --- 127 47.64 THANTI SP. 382. 16.4 0.. FAMILY F 4t N I C l b 41 MANPHV66 6 & h t.U I N 6 A -- - -- 6l. 80.2 0.- 26 13.46 FAMILY CLICtulnAE 127 $5.28 ;% GLYCtHA A4fMICA=A 153, 30.6 0.- 9 FAulLV 60NiaplD&F - -- - - - - u ,Ci im Sr. 26 n.3 u.- 25 ii.45 -g FAMILY Mt .s illk l D A f - C.YPflh HutvleaLP4 121a-- 2S.b O.*-- Sie 25.46 . . , FaulLi LuanW I tt.HF.! D AE LieuMNfhtW15 SP. 17e. 35.1 0.= 102, 42.61 y m a r.t bo= I D a t. ---- -- - - - - - - - Faalby m a GF t,nh a PFT T I M0kE A r. St. 10.2 0.= St. 22.74 _ F A d ll.Y 4 & l,D A N t il A E A R I O T Ht.LL A M UCOS A -- - - -- - --- 4 t h . 9 8.) - G. - Ib2. 143.4% HwANCHitlASTCH15 AMERICANA 229. 45.M 0.- 151 60.80 FAmlLV % > k t I D A t' -1 25 ..le Ct W AT*.hFNt i s 6P. - -- --24 b.8 0.-
.)
17s. 3S.1 0.= IS t. ch.40 L 4 t 814 t h t I s CU L W t k l 30.6 0.. 102, 4$.SS O k>hEIS ACUMINATA IS t.
)
PI, A I V We wt.16 bumt M I L I I --- -- 621 Jh.b u.- 123 h6.94 _ .. 2 11NID. SP. 306 61.6 0.- 102. 46.Ja . . _ . FAMILY ON'4PHlfAE 22,le DjelPATH4 ChPH6 A - - - -St. 10.2 0.- St. ~ C ONtiPH i s pt nds. ins t 6hM. Ili.S St.. 2h0 p9.31 tAplLV ohntellhat waPLoscatoPhos Honomruh 342. 1a.4 J4.- liv. b9.7J N a l%t ut l$ SP. 121 2S.S 0.- 127 56.14 16, 29.03 e S C s 'Li lP l.d 5 HUHH4 179. 3S.) u.. O O
I
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t N
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>= J 9* 4 g g E m 4 2 l" e$ 3 C
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3
- m == == es m e= se se **
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- oo **e == e e t *= * "" *' **
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- P3 % P C 2r e P P P P&C & P O 33? PfN P a ;1 3 0 4 d 1
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== N ** P "4 P M = = = =
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/:
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== 2 L FA e4 4 4 a.
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O 1 C == 2 4LULe
= - - C 1 ;r eJrJ 1 y4 1 == 2 3 E A C O e 7J1. /. d e, O 4 e..; = =~ a.
4 %L
*=
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> v. =F J4 m 4 > L4 T /> -a e.
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= == 1/7aa = n v* r
/ : 7 e.
a !- J -e
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l 6 O se s Y f r T E I T Z L T E T F I 1 4 4 4 e 4 4 es e 4 4 4 4 e 4 S T L 6 's a
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Table 11 - 1 . (Cont.) Lt)hbt LL **TCat> 4 e l'u V HASIN - Cu% TH r.l. h t ei se, T t siw tuuPTH QUANTFP FLaskIDA Pu-t h Co.* Psiw Al l um uutuaLL lb l T Tin a Cs ies t. Cn==u=tTT sfauCTune stunt At CarsTAL arvt= ru.t = eLA=T
-------- mu u nt w or i n o x v i nu a l.s --------
.------Pr nunne .yrr,-----. -.--.Fr wricnT---- ----n=T .tionT-----
(AIug N atAh bANCD STD D e. V TOf4L WFAN/m2 TOTAL WE44/m2 ran!LY mut.LIDAF HuLLA STWlATA 25 S.1 0.- 25 11.19 du LI, A SP. 255 S0.9 0.- 102 $0.9) FAMILY CAFCIDAE CAECUM SP. 25 S.] 0.- 25 11.59 tAMILt CWtP3DULIDAL Cu rPIDitt. A s* A ctrLO14 --- - -- - - 2 3 7 2. 384.4 0.- -1870 411.41 --- FAMILY CtwlTHIInAE C6HITHIUPS!$ LufRSO4) 25 5.1 0.- 25 18.39 CtwlTHIon mu sca mue. - -- -- -TS. %.1 0.- 15 St.39 --- h!T!um WAHlum 459, 98.7 (e . - 2h0 130.S9 s FAMILV CULudMLLLIDAE 1 n!Tyt'LLA LugAra-- - - - 3 0 6 . - ---- - ep t .1 0.- IS). 66.40 -- - - W FAMILY MAWG1hfLLIDAE GRANULINA OVOLIFOAMI5 127 25.5 0.= St. 18.0% [ u M A F G l h t l.1,4 APICINA ---
-179 - - JS.) 6.- 76, 29.9) 4ANGINtLLA SP. 2$. S.! D.= 25 11.34 F Aull y PYWAmlD(LLIDAE utenSTuele st* - - - - - - - -- $l. 40.4 -0.- 25 15.9%
Tuusoh!LLA SP. 25 S.1 0.- 25 II.39 FAm!LY v I TH I Nt'LL) D A E T P:ImuSToma SP. ~ - - ---- 131. eb.2 A.- 229 101.22 PHyl.um ANTHHuvuoA CLASS CwusTACLA 9.118 l.956 2.2454 0.44e1 SUMCLA55 COPIPuDA OWut M CICluPu!DA uwIn SPP. 16 IS.) d.- St. 22.16 - suMCLAss uST.e4 CUDA j u=In. SPP. St. lu.2 0.- 25 13.95 --s sueCLAss mALACt61WACA - - ' -- - onntp TANAIDACtA sueownt a kumusONOPHOW4 ' ugin. AP. 25. S.l -G.= 25 44.19 UNDt H I Si nPou 4 t AMIl Y ANTHUMIDAE umlb. be. -
-- St. 10.2- 0.-- St.- 22.18 644ILY SPHAENGMATIDAE usin. SP. St. 10.2 0.- St. 22.78 pupFw A=PHiruun - - - ---
t Aalt y A=PtLisCIDAL ugtb. SPP. 102. 20.4 0.- St. 21.31 . , FAmlLg A m en t La tCH l uaG - -- - - - - -- UNIO. SPP. St. 10.2 0.- 25 13.9%
&AulLT A=PITHulOAF
/
uwtu. APP. - DS). 11.) 0.- 821 sa.07 tAMILY AuMIDAF umlu. SPP. 4Sn. 98.1 25.- 2SS. 96.30 _ _ , tA=3tg a 4 T e 1 n 4t. - ' 0%ID. NFP. *> l . 10.2 0.- 25 13.9% 9 O O
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== Z O C D= >4O1 I M O e= /3 D.t O a=
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= = T 8 e = = S 0 t =w 9 e =t nt 5T V op Lr .
D g A a ) D TL l S 9 i t & A Dt 7 k T I nt 9 h n3 VaG
- h. ev I j h t F i w> Dl A e =
- l. t or h sG .
a c l r S CT T e t T6 wA F t 7 F f e Op 2
- P t. T =
t oD s A = Lh Pt t = L T h = t 4 3 s = 4 $. h L u=1 1 n I t h = t 4 - U wn = p 7 ( ou = 4 LT = t C = _
= -
t .
'o
= . m -
T = f S = 4 0 . T , - T S
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T 2 - n. _. t el t l u a w a t - , e , o n _. c T - n - -
+
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. T 1 = e 1
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=
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.
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> >J e 1 1 O N m 3 QW O *
- O 9 O O @ w A B H O O e B e e e 0 O O . *
! m i B
i tm S S I m! t 5 % e N
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- F
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& D m m N &
- O em=meda mm N W N N SNO9e m ** N 4 e 9 t a N e 44 wen G 90 N N 4 e m 4 4 37%eNN7 9 3 a e 0 J e O P e e e o e e o e o e e e o e e e e o e e e e e e e e e O g 8 e o m Ne a m 4 e m P e OwmMPSN N s @
0 9 0 9 O m S N& Psp e 4
- NT 9= men mN 1
N O 9 Nem N *3 9 N e 4 m t 0 w m 4 m E O B 4 & a 9 1 D O n 2m WP e e e e e e o e e e e e e e e e e o e e o e e e e m C2 Js e o e e m > e e N meNeemm #4 e O ms e m a e Neem a > re N 4 m O ##3Ne## Nm N
=
ONmOe # NO O m N N & C MJ D N e 9 N m
- m m N m m m em e se O A' ? e 9 e
2> we*
- 4 CC >d C 2 1> m: 2 4 4 4 4 4 $ D 4 B $ $ 0 0 9 0 4 8 8 8 9 3 0 0 B $o 0e e
4C 2 1 CC4 6 0 e e e o e e e e e o e e e e e e o e e o e e e 4 4 !*a 2 C2 e e e OJ O C C O O O O 0O30000 OO O e 0 Q O O C0000 O V = e VW k 2 e2 Xe 4 6 0 m Ca C1 ai s> e A CC 2 5 42 1; a 9 & m 9 & P m 4 &mteam2 me J % L 9 & 3 N 4 w eeOm 94 9 e o e e e e e e o e e o e e &e e e e o e e e e e e e e 4 4 n s 9 2 e eV e m m N e m e emAmmme a v 9 r 3 0 8 4 m 32 7 m @memm M e e m m m em N m m 3 N N Nm
- m m N @ N 9 E -d 2 8
- m *
- C 1 g e E O N J C3 0 G JM e aU t 2 3 4 2 o e e e e e o e e o e e e e o e e e o e g g e og e o e o e e e m mN &
> e & 9 e 9eEmn 9 me e a m 7 m
3 m m N N &&*=m Cweee#e AC N 0 m O N ONa me m ?* e e m N O m m 6 2 N N m m m mes N = e % m@ * # N m 9
" j l ,
- I i ,
w i ,
= l i
i , 7 3 K 3 C t 2 L 0 M =
*
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c cs= 6 4
=
C uN 2 U
=CE ' a e l' J
=
42 60 o w W W 4 w i 2 2 N L-6 4 4 e4 2 2 1 1 OW T e s'*4 6 d e ' OWen J= W 4 2 2 1C at C 1>> K 4W 4Jm>: =J 4 >= 4 de e4Le 0 404 4 CC=414 C HOWUad i 1*=C 4 =*U AJ4
^ W E Owe = 32 C a2 44 4 M OUwi O w 64 3d = 4 12 AOkm 4 10 0 e
==J4 4# J d 2 2C20=A =% =>CI WMU=d y, e I =
1 J2JUODe : Owd ===> FAF .JT 2W=
=C124 0*AOJ *=
em W W 4 03Z=
~Y*=
w 2 4 J-4 => k e=242 5 7 4 ==01> eJ=2 -Vela er 0
- e e "d > eed MeUA> e4 1U W4
=02 tX 2 **4 2J e 1J 2ve d OJa AA4 *M 1 1a4 24*
- s * =
T 1 41 2 6 1k &ew J2 4 E12 C=dev2VWW4 4 d e Za 441J4 I 4 W2 3 2O2 2 0 246 ? 2 if 2 ail V V O 2 JM W 2 #=
= J QT e EJ4 A 2 C E ww2m DJssWr=4 C=w4 Cd I2 26 4WM2 2===>
2*=1/
*C*TC e Z * > e M O eI4 Z WWFK =>m 10ma eUw40TJ4IwJT =1 V > 3 JQ>F
- JE 2 Wa FWC 4 C44 *>O 11 C I =C 3 34 JOCU 2
= 2 2
- 00 *
>= => m J=> e 4 M2 > 1 1 2. x .2 8; ,.=1-U =, 2 2-2.1 M.
. M. O. w2-r--- -2.1--2.O. .w= ?. 1 e -2 J2204JJ.J-J......
e 24 .2 JO O 2 J: CJ.Ju=zs=J-JJ, J.Jud2 2 21= JC: J:
- ==
= 2 1 ,. = . e 1= - - = m = = = = = - - =
I
=
f
, 2 E E 3 x r F 2 w .I I. T. - .UE F X m
I f db b w
.E a
F. b 6 6 4 6 6 4 s 4 6 A
- O E W y 20 2
- J = CJ A. <
-- J
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=
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< ' t i n s L L 2 ,
I=B-38
Table Il- 1. (Cont.) C0hst LL => TC ALP L e001 FDubfM QUANTip wtPahT Fou
- MAsim - DISCHANGE 6LOh!DA CDet h CuspouaTIph OnthALL edTTue CudF Cou=uwfff STPUC1unt STuor At ruv3fAL wtvrp rostn PLagt
^
------==huMHfR OF lhDIVIDUALS-------- '
- --- -------PPp 3 04 A p r
- r t t e ------ ---=tET artCHT---- ----DAT kE10HT-----
pEAm NANGL STD L E *. TOTAL stAm/m2 TOTAL #E*h/M2 N
- TAnO4 Fam!LY n#RI4110Ar 153 S6.67 - HAPLa% Cut 0PLUS R0nHSTUS 260 40.0 0.-
NAthtpEIS SP. 16 10.9 0.- 76, 29.s7
---178 TS.S 0.- 76 29.40 s Cn t.n P f.03 WH*WA , Fam!LY onth!IGAt 24S.76 Ost4IA tH5IFOWu15 73d. 105.5 0.- 662.
Fam!LY PAWA04tDAE 1816.62
, Aw1CIDFA PH It.Hlh AE 8403. 1200.$ 76.= 32e$.
A w P C I nt. A TAYLukt 3387 4t).# 102.- 1375 463.06 ANICinFA SP. - - - - - - - - - -
--------95, 3.6- 0.- 25 9.62 - -
, PANAON10E5 SP. St. 1.3 0.- St. 19.2S FAMILV PECTI=4Mit0AE 9.02-
- 25 r4 -3.6 6.-
PtCTimAw!A Coubott e 25.--- CC . FAMILY PHILLODOCIDAE 25 12.43 8 PNVILODOCF AHt=AL St. 7.3 0.- Partly Pot CILOCH AF?]D AE -- - d$ l$3 21.0 0.- 127 47.48 PueCILOCHAtTU3 JOHNSON! FAMILI PnLYholuat M A p =oT Hot. A cut,t A T A -- - --- - - 15). --dt.9--- e.- 76 2F.22 FAMILY POLYONDuMTIDAE 21 12.43 POLY 0mD0%fts LUPINA St. 7.3 0.- FAM[LV StatLLlDAE - - - - - - CH'thF HO%LMI 127 19.2 0.- 76 31.92 2$. 3.6 0.- 25 9.62
%AntLLA mICwoPTHAL4A
_ _ __1 FAMILV S P I O* I D A L - PANAFWlUNOSPIU PIhd&TA S35 76.4 0.- 290 101.m6
7.3 0.- St. 19.25 '_ ErJ POLIDUNA utB57Fnt St.
Pw gogose to ut.Tt wane AgCHI A - - 127 - Id.2 --- 0.- -76 39.92 .7J) ~ SCOLtLFPl5 500AeATA 407 56.2 0.- 191. 121.h7 280 102.76 y SPIOPHAmts MumsyI 433 0.- o,io. se. .- 2 6. - 61.,8 io. - - 0.-- - Si. 20.04
- ;,j FamlLT SYLLIDAE 109.e8 stLLIS SP. 418, 65.5 0.- 306.
CLAS$ AwCHI A=ht LID A - - - - -- -- 53. ai.e o.- 76 37.2e _ _,; m. n=io. se. , PHILUM MdLLU$CA 7.232 1.03) 1.2195 0.4656 _ _ ;7 CLA5% MIWALWla _g FAMILY CANDIIDAE rj t.Atv1CAkOgon nowTout -
----25.- 3.6 -
0.- 25 9.62 FAplLV MfflLIDAt -
25. 3.6 0.- 25 9.62 35CHaolua htCowvue - - - - ---- -
FAmity mucoLAmIDAE - - unCuLA=4 3r. 2S. 3.6 0.- 25 9.62 qg)
~
FAmlLV Snt.t CUh T ID AE . C'J T 466 t **5 plvl6HS -- 2 5. 3.6 4.- -25 9.62 t amit Y TtLLlhabat
~
ftLLINA SP. 102. 14.6 0.- 76 28.67 2.292 0.327 1.61w6 0.2314 CLA5s G A si w oes.ba
--~
tA*ILE ACit aC I N ID a t: ACTtoCINA CANALicutATA 560. u0.0 0.- 260 107.4h 9 G e
I _. I 9 eM 4 2 3 4 % @ mJ t E M ea 9= 4 *e
.% as IW
- as 2 t.J &
3 ed ** O OP es O s Z
- s. > =J 3 24
- O fJ>
C 4 O @ he 0 > # 3 o e O e EN 0 E 9 % e to 2 e I as @ e Ce
== a O aJ B
9*
*J s as O 4 ea O De O C se 89* e 2
er 4 f J 85 E D @ "to e * @ #
% M # '98 M SI N N **
aa 8 9 m Q Ne #MN N P* 4 4 P= N d 3 mig se W D 9 9 O A 4 3 Nd4 4 4 S 4 M 2 4 4 e o e o e e o e e e e o e o e e e O e 9 e o e o e e 1 e 8 O 2 @* PPP P P 3 @ S 3 7 @ @ F 4 ee > me 2 em 7 m M == = es e o m 7 *= 3 # > M == N en 9 8 eC se E M 0 .E D aa 2 es e1 9e e e o e e e o e o e e o e e
> 0E J* e e e o e o e e e 4 e=
# o i_ e == 3 # # # # 4 N # C 4 C 4 s Po # == ** # # N e N e P= 4 e J ==
De .3 3 Q Mc # N re re N m M e e M rte N
.O. m a 4 4 Cb =* 9 c en 3 Se ** 3 4 J O fl D 4 C 1 1> e= 0 2 g e e 4 9 0 0 0 C O4 9 0 0 0 0 0 e e t 9 4 I
- O 2 t 6 e e o B
e B e e e e e e o e e e e e o e e
. ao OO 2 rz e o e e C
O O O 3 O O C O O C O O O 3 4 V == 0 CO OOO O O Ve 6 &
>2 2 4
- ei
- O+ CA I 1 e> e a "") O E 9
.J J &3 .eJ t e 4 4 N 3 e P *e 3 m J e L 5 e e4
- e3 J ' d a e e am f 4
e * *
- e e a e *
- 4 4 f3 5 3 2 * * * * *
- e * * % M J B 4 9 ** 9= m m **
- e e m e m est et am a 3 46 O 2 2 3 3m g c en N f == hl X 9 at se em sa =in ,
O 1 R. 0 1 1 V O3 4 e
.J t* O
= U e D e e e e a e e e e e E 8 e e o e e e e o e o e o e e e N f Pie en P @ O D Fw D em 6 e b # d' S O & P6 Pm 9 ee
#1 8 E
2 O 9e O #t M N N to O - M c *t Pe 'N N ce a a N e N 3 e se se se # - 4 N == = d be . j I l 6e I f i i l eie i , j g g R ' l l 1
'I }
0 i ; e 5 l i C I i U \ l l ! 01 % 4 ee 4 - E l C l 4
. a,O e w r i 6 m i 4 ) l r w .a i r
'i O ar as s c se ' 4 9 ! led 4.1 4 e3 4 0 4 O a= me ag Al t= 2 Y es k W 4 OO2 ** k =e .33 '
O 4 W ' O 1 43 O 4 *E o er O I O 4 ses em O O C 4 m U as eJ4 30. =E 31 u 2 J > 3 & ^ a= *Wk J4 ' et 2 ee == - .1 2 3 4 O == ==
- b14 4 OW 1 4 k O * ,",,, C W 4 4 O be .3 0 4 O O == tfl O + *=
C C JF ew O4 eO O eA me e ** ? m 2 O=e 4 em eI e4 e2 e w OA O == O e 6 e .J 1 > 1 0 11 'l e.* E ** 3 e == 4 4 4 a ==4 x en me O 1 == eL1O k 1 9 1UC eO *
- 0,
** 4 Jo*11ma.3.JO4CF4 em C ar 1 e- 1 0 14 1L4 # 1 14 4 & F 14 I 1 > 1 0 1
- 1 - a en 1 01
% /: *OOOIJ2 == 2 I O a. . OA i1 2 44 .eJ 4=eA 7 f) O e= VJ C V O e= 4 00 it) 1 2141 it' I t2 /.
s *0 T *i J F.
- y 2 4 O zCCOOJ4 J ee 0 1OL 2 04h J V O == 0 E O2 == 3 I C O M
- an as O e7 e er e e 1 as *- *I e* *4 e as *6 4 E2 04 04 e y
Z me C4 sa 4 J L **&11 == == O 3 + 3E Oa> W t >+VJOOOOO1 F O O2 O OO
.Oe =1 O1 0 C
== ** ** * ~
O O O V y JJ w4 4 6= 4 O Oc 4 as > - - O e.e se 4 2 == 1 = 4
/. a > d >0 0 2e &3 Z > ** De 2 De C p= 0 V2V2 2 :./ > O> F o= 'a ?
- 2 =* > 2 > F as F > 2 > F > 2 > 2 e *Z "O O eJ T ~3 E. I J V V U ed T ee e= =e w ==J
* * .J O en Z 3 f as V y=
D O/20 4 m A =e.J O- J C QOO O 2 x ==JOJO = OJOJO *= = e= -
*O .4 O
- E 2. 4 4 2 1 7 2 O O 1 F F 3 5 I E E 6 E E I I as 3 4 as 4 4 4 .E g J. ;a,, J .J 4 er as a r r . as 4 4 4 4 4 l 9 vcm a cO O Cw O s . A weuo z w w A O U . .
= 20 2
- k .
Of K 3 1 1 K E .1 % A S 1 O JeOC C O OO C O O
.J **k.
# 6 et me J y) v W A 4 C 4 Z%
= C O h 1
.e e H I-S-40
O st - .I ' ,)
# ' I i
' l 9
8 m ' 1
' , i "l ', ! (', ' -. J B B ^ i, -
l , 3 8 % * '
\)
',,)' '.
. e.; ea e L e -
p .J >4 e 2 4 3. es. O e z %1 5 e 3e se * c 'm e
- B I
e e= J 2 8 e O
~
C> e G 4 .L
- w 0 to .
M 9 l
- I m 0
0 m i 0 E 3 W
- 0. %R @
K4
- V ed i e
== a e u
E
> l LJ t 3 et @ l l e o -
i De 0 Oe M 2 9 >
- e 3 m J N k
D
&. 0 3 ai e N em # (k N
- e9 0 g c, <3 4 e N@ 9 C O e g e o e e e e e to 0 0 .3 3 S * @@ @ O O O > i"e *
- N 2 9 O A e 0 3
> 0 se 2 == 4b w : 1 a s e e e e e *
- c em e a se e e == # # a=
a to e1 3 e N **e eN N @ m 4 4 Cb 1 > se 3 W l j , A C9 >eC 1 1> ** I # a C 2 3 C f* e 9 9 9 9 0 0 9 _ aCb a r. 2 e e * * * *
- 4 V se O O O OO O O O> b &
>3 34 % e a G s ; L s 1 e> 9 e CC 3 4
- J E AO me 0 1 a De & G 7 4 & M@ d @
4 M a e e o e e 2 ea u , . 3 .e .a O
==
- .e
-e - . O ee l .
O E S S E l u : : . i a $= 0 aU G ' 3 6 ! ' a e e e e . . e e l k 8 e e a me or d .l i , t i M S 2 j e N e @M N ' M i ' i .
! I I '
,le
. f j ,
em I a i
} 1 r , l 3 i I l ! i r I f I 3 i i !
6 O 4 l ' i l l ) e ., I, i E 3 0 W I M l j l l I z e' i i i e f W 6 i I ' UW T i Wee & e e e ZO , WL
, C QO b om W2= e *J es to ;W W es a e ==
j 4 C Q >1I eC : k D* m os el 6e A=wa y at [w w De e4 U 'd 7 O I 1&4 e ed 1.3 & h # $* O O 6= 4 3 e 3& V J J W ; & 1l= rera3 4 W W W 5 W CL me ! em SE 4 4 e2 O e 3 eg g "* 1 as es gL & e C e e I L eu Q 4 1 F r ze > et C J3 es e.e
, AW me r e3 se == > == > 3 = .x F == ZF
**2 e3 3 eJ I J & e.3 W W 0 : V3
! C ee == == ==
e 3 te; M V F X E f E O e e W = = 4 x y a w cm w w : a
- r: y = a 3
== to C O a 4 M be as De - eo n x C Z he %
b'
- I-B-41
Ta bl e t, (Cont.) Com h,t L t. 4 t T C a l.t' L t !'D Y MasIN - '1- h t Pilw T Fow fouMTM GllAkith HliTTom . Plow!DA Fus t w row eni> A T i tip OWL 84LL Com= UNITY S T M tif f t'M t* STtIDY AT CWVSTAL MIVtM PuntM PLANT
========NUMbEN OF I Nfil V I DU A L5 == === = = =
=======ptp sot: 4 6 M m F T t'M -= == = = ====wff ht.1CHT==== ====091 teElGHT=====
T k,/ ON N MtAN NANGt STD Lt V TOTAL P t' A N / M 2 TOTAL MLAN/m2 tnt Ab --30099 4Jv9.9 1935.= 4441 25=t,95 91.)42 13.049 26.7660 1.623)
..-e, - e.-,e
-*. -.,,,.. e-. -*
** - " * * " " ~ " "
-- __- we m.---e - a- --
l a) I g, _-.-...- - ..--- - -.. - tQ
-+%-- +- - +
- - * - + " " "
.we...-- *_- - - -- .--r -ee--+ e +-.---
9 I l
-ee me
_ - b
Tat B-2. Basic statistics for each taxon and wet and ifry weighta for each group from v* ai suction samples of 1978. CohmtLL MtTCal.F & EDDV W o.Pnk t f ou FIDST GUANTIN H451w - 0011 p ut.
- - FLOWapa P0mple COMPoaAftok OWLEALL
! ve=Towl ConsumITY STPUCTurf STUDf AT CWf574L DIILN PostW PLANT i
==------mumbia OF IhD!vipuAL3--------
=====--PER SOUAHL METLR------ ----WET WEICMT==-- ====DRf wEIGMT-----
NANGF STD Ut v TOTAL MFAN#M2 TOTAL MEAN/m2 FA&nn h atA4 I I PHil,u. 61.441 12.26s 22.sler 4.seis PontrewA '~
- 2. .' O.431 0.2654 0.0$31 PH t t,Ha S t eumC*iL A SS. 11.0 0.- St. 22.43 uwlu. SP.
II.III 2.428 2.2394 0.4477 P H I Lilm ANhEllDA CLASS P18LT CH A t T A - - - -- F Am it.f Aut = p roLin AE - - - -- ANFNICHLA CHISTATA 1. ).2 0.- 1. 0.45 p FA4ELY AW A HE L.L E H AF 9e 1 ., 8 Ge* 4 l.4W -- - y AwAHthba I M I Ct'* ou -- - O. 0.- 1. 0.55 m ,. SCHl570atWIhGH 8000LPHI 2. I F A u ll.f CAPITFLLib4E D i
=* p l epe 46 Tish CALIFouetEN658 --- 4 .6 0.- 8.79
",g SCVPMoPNHClus PLATYPHOCTUS uulo. SP, 36 S. s.2 1.0 0.- 0.- le. S. 36.80 2.24
'~~~
fAalLW t.UFICIDAL --- --- MAMPNV$A SANGutmEA 46 9.2 0.= 21. 10.le FamlLT FLAMELLIGEN[DAE PIHuelh tuuCA -
- 8. 0.2 0.= 1. 0.45 F Aa lf,V GLYCLHlpAt GLVCtNA AmeWICANA S. 3.0 0.- 5. 2.24 -'
~ ~~ ~
~'
t'AmlLv CON I Aul D A6. - - - - - -
- 2. 0.4 U.- 2. 0.89 C L Y C l a t> >. 5P.
FAMILY LuuBRINEREIDAE --{_-- Luanulntul6 6P. -2. O.4 0.= 2 0.h9 lAMILY MaytLONIDAi '(
mAGtt,H94 PtTT!HONLAE 2. 0.4 0.- 2. 0.99 f'A4tLI MabbANihAt - - - - - - - - -
- 22. 4.4 1.- 7 2.61 Att0THtLLA MilCUS A ..y uw&WCHlHA5VCHl5 AMFRICANA 41. 6.2 0.- 30 16.78
.'.J-FAMILV es t W L l hat - - '
- t. A t omt N e'I S CHLV LH I 1. 0.2 0.- 1 0.4S N 6 u t.15 FALSA 10, 2.0 0.- 8 3.46
- se 6 W h l h bucc t hb A-- - - - - - 80 2.0 0.= 7 J.On -
]
P t.4 Ty ss6 u t l h numERILII 1 1.4 0.- 4 1.9S f 3 HalD. SP. 21 S.4 0.- 21 12.H7
-l F A sel s.y n=asPw l o A E - ------ - - -
DlHPATHA CHP=F A S. l.0 0.- S. . 24
- 9mHPHis htHUL,054 114. 22.h 2.- 91 19.3S - ~)
__3
;- FAMILt uhMINlluth- -- --- - - -
HAPLn5COLOPLos pomusTUS 9 1.u 0.- 4 1.79 7
- 33 6.6 0.- 28. 9.58 ,
l MAthewfl5 SP. 6COLOPbub Wukua 8. 0.2 0.= 1 0.AS P a p a n'410 A 6
- M_
F A u l t. g ;n-- - ;
- Paw At e l e ,6 N SP. 3. U.2 0.- 1 u..S U
F A = 1 t.y P. 018 m Ah l I D46 P t C T I N A *e l A Coots'il 40 2.0 0.- 9 3.94 tAmlLV p Hit LaDOClpat 9 e re.NE MtftWupun4 1. 0.J 0.= e 0.4S O
Table B-2. (Cont.) CDNN t Li- "t TC Al F 4 DDDT wtPhpf Fow FIp5T GU4pftp n a s t i. - rai% r ml. vtmtowI tLowIba PiJet h CO M PinW a T I Dh OwthALL Cow =uhlIY SThDCTuht 5T0DV AT CNt% tat, MIvtM P h e t. k P L & hii
---- ---edms*t.H OF l h f > I V I DU A l 6-------*
-------Pep Sou a r t. mLTt.W------ ----ett wtIGHT---- ----Det mEIGHT-----
N ptAm N A u r;t sin t>t v TOTAL pftw/m2 TOTAL ptAN/m2 [Asom e 4 4 [ L. f Pitt C i t.it( H a t' T I D A E tant C ] Li tCH A t T OS JOHN 5oNI 6 1.2 0.- 6 2.68 t a w t i,V Pitv%ognat n a = e l er it ACULtAIA 1 u.2 0.- 3. 0.4% 1.t P t 0 & *
- f w l a t o e g e g s a L I S
. 23. 4.6 0.- 11. 4.de t.t P I don 4t f Ui V. j 2, 2.4 0= I2. S.$)
>Am[Ly % A b e t t, t D & t.
C ein a t. 00%th! 3 0.6 0.- 2. 0.b9 eas.eICta v. 9 3.b 0.- 9 4.04 S A h > [ t. A 4[CHOPTHal.MA S. 1.0 0.- 4. 1.24 ti s t D . dP. 5, 1.0 U.- S. ~./4 4 [ t 4 '4 i L v 3CablHht 6d f Dat u.2 0.- 0..$ m o,iu sr. i. i. 1 F a 4 I [. ( Se k Pul,ID A tl y t*g t te , w. F a u l t. f SpleudlDAt 4 0.m 0- 4 1.14 A Ps aPw i s p94 nse lit P y G g A F. A 1. U.2 U.- 1. u.4S pol i onw a -t. tad t e p l S. 1.W 0.- 3. 1.41 Pwtosh5Plu Nt1FNOMWANCHIA S. 1.0 0.- 5 J.24 ONID. %P. 1. 0.2 0.- 1. u,45 FA=lLv Syt,LIDat P. s o G o r. *' tINPAw t. l.6 0.- 6 2.el svtL!s SP. 33 b.6 0.- 19 7.47 umiD. 6P. 6 0.2 0.- 8. 0.4S PA4iL! f t H t.H t t.L I L A E PISTA CMISTATA IS. 3.0 0.- 10 4.24 Pinfa paLanTA 22. 4.4 0.- 20 M.73 -
$ T w t a* Lie %f l* A HANT*ANAF $6 11.2 0.- 26 II.S2 (i _,]
neto, se.s 2. u.4 0.- 2 0.e9 7-PI 7 ?,,Ilm mill L81$C A , class aaPellNeukA 6.8St 1.370 2.0164 0.5633 F a at i l y a r a w t 644C H I T 4** I n & F a c A ae rei.icH t t o% A PvGantA 91. Sm.2 0- e2 25.40
>AmILV i SC 6* Na sC H I l s a8e l l) A F.
E st e+hoL H a ro% e A P i t. Losses 284. 57.m 1.- 11 2 16.$3 C t. A s s nIvatytA 114.242 26.6411 102.3202 20.4640 F A a l i, V a
- C i n s t.
awCopsis ana=hl 2 0.4 0.- 2. 0.e9 6 A
- I s. v c Awot t hat
- 1. A r v t C a m b l u e auW THIA i 19 l.M O.- 17, 7.41 D a
- I ta Caahliluat Cawni t a 4t h a FI.udluANA 66 13.4 0.- 46, 14.12 6am!LV O 'p mis t. g D A F Co.ws H.4 1, W . M. 1.6 0.- 8. 3.Su t Ae ll. It=lhA>
LIWA Pt LI.HC I D A 2. 0.4 0.- 2. 4.hv
& A 411. 5 t. f a en. b l lin A t I.f tl% 51 A e6 V A f. l o t 3 0.6 Q.= 1. U.SS
* > a < t t. y wac twipat foot 4 s io = 4 911os. isi telu%n. LAST CODA lh 6 E A >( se eAE 4S200060 ian tas*i e i't d h o.t 45/o.ut*lluo
- 1 u.2 0.- 1. u.4%
Table B-2. (Cont.) CO%hti L e6TCaLF b & l'D V dahim - CD47WHL wtPhh? thw fl85T OosuTLD UttTONE I L4 tW I D a P u
- t r CbbrukaTIDb OWLhaLb C0amumITf STubClume stuDI af Ch15faL hlstW PO=en Plat?
--------mventu 0F Innivifioals--------
-------Ft> sms a a t etTik------ ====m67 mEIGHT==== ----Dat mEIGHT ----
latum a a t. a h RahGF hTU utv total mEaN/u2 TOTAL etam/m2 Fa*ILV m f 7 8 L l e a t-15Cdantum wtcuwuom 20 S.6 0.- 27 18.17 eo9CutuS LeftWahl9 - 0 l.6 0.- S. 3.54 FamlLt usteFibat 05thra t.o u t .s r u l s 130, 23.6 0.- 120 S2.44 FamlLY PtCTimivat ambuPtCTi% I=WaDia=$ l. 0.2 0.- 1. 0.4S fa4ILY StutLIDat C ua l *4 t a Coa >C t a t a --- - -
-3 0.6 0.- 3. 1.34 StatLt PDwflCua 41. u.2 0.- 31 16.19 F a = II.y 76LLIAlust g4 T.LLI a sv.
.ia- 0.2 0.- i. . 45 - -- .
cc fastLt w t 4 t' h l D a t i Chine CahCLLLata 1. 0.2 0.- 1. 0.45 4' Tma=3e=#Lla condaptha- -l. 6.7 0.- 1. 0.45 (Lass Lastwarous seeeeeeeeeeeeeeeeees 69.2612 13.0534 FaeILT Haml%DFIDat wa=Imi*ta he. --
--4 l.6 0.= 0 3.S4 - -
FamILt puLLlDat mulla 57=147 S. l.0 0.- S. 2.24 Fa=ILv Cee P i r+ubl oaE - - - - - - CwielodLa aCuttata 29 S.m 0.- 29 12.97 Cwt PipitLa maculosa St. 3.6 0.- 9 3.93 CaePIvuLa eLata 320 64.9 0.- 147 63.58 FaulLt C t W I T n ! ! L a t-
, (-d
, .,/
CENITHlum mu5Canum 8. 0.2 0.- 1. 0.4S F a m II. f ChbeedpeLi,lhat - ,---m a%aCwls 3*=IFLICafa 1. O.2 0.- 1. 0.45 JZ q:) alfwtLLa inmafa 1. Q.2 0.- 1. 0.4S --; taalLf FI66eatteIDat - - - > ploDoda Catt'* ENS!$ 2 0.4 0.- 8. 0.5S ~~ ~ Cl
" '2
$ a d l l. V =aWGINtLt.lbst macGl=,LL4 aPICl=4 12, 2.4 1.- 6 2.07
-~
taatti =ei.a%rLtinat atl446L .. Se, l. 0.2 0.- 8. 0.4% taatte ethomweWIvat
,ti.n=ce a Como=a 1 0.e 0.- 1. 0.45 _-
# auls y audICloat CataTwe.Pwow Ohfatahum 6. 0.2 6.- 1. 0.4b i
pH gg on a w (nwnpe tua . :_ Clash (w6eTafta li6.vle 23.364 40.2558 8.C5&2 .' ; st6aCLass ClealPtola F a u l t.1 maLahtuat iU
- m a i.a =u A 6P. 27 S.4 0.- 24 10.4m -
sanclas3 w a s.a Cos t h aC a Ow ne = Cn= ace a t a d t s.t n i a h l f L i b e t. n%1n. ske. 3. o.6 0.- 3 1.34 nhne w avsluaCe a omlo. AP. l. 0.2 0.- 0.45
Table 11-2. (Cont.) O Ctih h t L1, a t T C 41.6 6 1 I)D V FIR 5T OuaHTkB h t PH64 7 thw OVERALL H A s t ** - Cn" Idol tLUMBOA post k COMPuhATibh . vtwroul CommdwlTV S T Nis C T U N t. 51001 AT CPV5fAL HIWLH PunkM PLakt e
--------mumHtN 8 8F INDivlDUAl5-------- ----LNY WL i t.H T ----- .
-------PkW 500Akt utTtH---- -
----WLT WilGHT==--
70741, MEAN/m2 TOTAL mtAN/M2
. h ht AN kA*GL STD btV Ianne . ou t> t ie TANAIDAC64 sonowbrw tilp DeswHow A 2. G.4 0.- 1. 0.S$
awlu. dr. sonowotw nosonowoPHowA 0.- II. 4.71 g 33, 2.6 uglu. sv. puntM I stnianp A FAMILV CINOLANIDAE 32. 2.4 0.= 1 3.16 O u=ID. SP. - - - - - - F 4 m i t. y linit F I D A t-
- 2. 0.4 0.- 1. 0.SS H w lia. SP.
Hg nkut w AmPHIPonA - - - - - - - - -- Aw Pe t,5 bC ib A t. 3. h F a m i t.v ohlb. sPP. 7 l.4 0.- l.52
- g AmPHllDCHIDAt. 4 1.19 b F Am tl.V 0.4 0.-
4. O unlei hPP. FAMilV AMP 11HOIDAt 49 9 . 11 0.- l#. 7.50 umlu. SPP. PamlLv- AowinAE 20 4.o 0.- 7 2.67 o=ID. sPe. O FAMILY CAPa*tLt!DAE 9.2 0.- l. 0.45 I. UNIO. APP. tAMILV Cow u P H i l li & L U.4 0.- 1. 0.SS 2. o m i ts , svP. FAMlbf dtblilDAL -- 12, 2.4 0.- 4. 2.19 UNID. SP. g t A u li.V PHLIAhTIDAF 0.49 C, 2, 0.4 0.- 2. ,) tl=ID. 6P. I '.
& A M il.f PNilauCf PH AL I D AD 0.- 2 l.00 g S. 3.u u 410 SP. --
0.45 Sit uisTHo ll> A L taalbf 3. 0.2 0.- 1. e D41 n . SP. g OWbtW Ok C A PilD A ,,
> A s* I I y AI.Pwt ID AF lb. 3.6 0.- 9 J.91 ALVMtHS AN *l Lt. A THS l.2 0= 3 1.30 U A t.Pb t HS He it H uC H all.15 6
U.= 0 3.$U 18 l.6 0.W4 A LPu t U F. h o+4 m a a h
- 0.- 2.
4 0.8 A f. Pet H N SP. U F A M il.3 CALLIANA55tuat' 3. l.)G 4 b.g 0.- uP* 66* H l a ADFlhlb - O . ~/ 0.- 3. 0.4S 3.
+ p.10 SP.
tAalL1 HIPPinLITBDAL 24, 4.8 0.- 11. b.36 H I P Pot, V it. Pl.tHHACANTHA- 0.eS -
- 8. D2 0.- 1.
M l P Pill I T t'. SPP. 4 D.h 0.- 2. 1.10
- T H JM tl.4d!DANHS F A m i t, f " A.II 4* A t 1.64 -
6 1.2 4.- 4. Li n 3 41 A DOMIA t A M l l, V P A L.Hu l O A t 12, 4.04 22, b.4 1.- . P A4. eld H N hPP. F A a814. V 6' A l. A t a s lee l l'J A t U./ 0.- 1. 0.4% 8. V a n. A t ralfe 6 tleH I D A Nil 5 W
Table B-2. (Cont.) Luhht LL a6 TC Al t & Aony h t.Pil> T F f th FINST Guauf t h maslo - runTwiH. OvakALL v t as f ow I tLowIDA Pumaw (p> Pop 4Tlud ru=MUNITV 5ThuCTuML STupy AT CMf5TAL P I V t.R PontN PLANT
= = = ----- se I n n t N OF I N D I W I Ou t l,6--------
-------ptp So u a p t. mpTtp------ ----=FT WEIGHT---- ----DAY wt.IGHT-----
h at Ah hA=GL LTD LLv TOTAL mEAM/m2 TOTAL miah/m2 jaann Pal.ALMONfff5 IhithatDlHS 2. 0.4 0.- 2. O.W9 palat =Ohtits Put;10 1. 0.2 0.- 1 0.4% pat.atmo=>Tes $P. 1. O.2 0.- 1. 0.4S P e_ w l Cl. l a t'h t s [J)hG I C A U D A Tu s 2. U.4 0.- 2. o.b9 u4to, sp. 2 u.4 0.- 1. 0.5% FaalLY P t'n 4 t'l O A t PtmatHS SP. 1. 0.2 0.- 1. 0.45 FantLv PlamuTHENIDAL etwalaa 3P. 4 0.4 0.- 4. l.3W
$Aally PakO LLANIDA).
Pt THat.lsTMt s $P. 1 0.J 0.- 1. 0.45 H tAmity P aeoC E d61 p a t - - - - - - --
- 1. U.- 1. 0.45 hgi A M H l ut. a f t' u 51MaLTalCOS t' A M I L v AANTHluat 0.2 4- >HuvPAmeWtub DEPkf66u& 240, 48.0 0.- 102, 4S.98 N 4LUPANHWL PACpAMut 9 l.b O.- S. 2.17 henPANOPE I t. s A N A 18. 2.2 0.- 1. 3.19
- 1. u 45 -
4 tioP A n*)Pt' be. -1. u.2 0.= P440PLd5 McNHSTil 3 0.6 0.- 2. 0.u9
- 11. 2.J 0.- 6 8.08 M E THunPamurt us H AHeelst l o%in. 69 ISS. 31.6 0.- 66 10.49 15.213 3.041 S.7929 1.1566 P H I LilM 6.C H I Ntid st. k m 4 T A uslu. 69 9W. lb.b 0.- 66. 37.43 , __.
' )
PHILUM CH0PLATA 251.512 St.506 31.2188 1.4436 -T5's rs. A h6 4ACIHIACDA nigu, se. 131, 26.2 1.- 66 21.14 Cl,a s s 05ftlCHinTL5 25.162 5.072 4.5643 0.9129
--44. m.S 6.- 14, 3.Se ~
-t u=ID. be. ---
,) -
J
,-88
-= -
o O O O
Talil e JF.? . (Cont.) r 016. = 6 L L atTCatt b & 0811 4 wasth - Cl am t will, ei t Ps ik T tow 6' I W 5 T Gi> A Nik k OvikALL vtmTDM3 iLbh!DA Plio t h CsaHWOM ATION CommuMITY L T k t;Cl u w t. S TilD V AT CwfSTAL HIVLH P0nLH PLANT
--------nUMHtw fir t h f 6 l v I bu A l.6 -*--* *--
-------FFH s uli n et t MtTtH------ ----ULT mLIGHT --- ----Opf WEIGHT-----
N M k. A W RANGF STD t> f. V TOTAL ktnN/m2 TOTAL NLAN/M2 T A Lil'd 7074L 2776. $$$.2 153.- 1139 478.50 ******************** 247.6769 57.5354 4 O _. _ i .__. . _ . in v' e Co O -- o I e i 1 u r"'- 4 3 ...._ go O es ed
Table B-2. (Cont.) Cohat LL p t T C A L.t t t Diny WEPouf Fow FINST Quauf t k HASIN - u t sCH A wGs. OVLhALL W F N TIOr i Pbbw1DA Pdwt M CUWPlikATlHN C n m allN I T V S T R u c T u w t. hTuut AT Cuf5fAL HIVEM Pile t R PLANT
==---==-NUMtitM OF INO3V(DUAL 6=====---
------*P&H $9HAME METth------ **=*el'T wt'lGHT --- ----DHf u t. l G H T -----
STD Ot.V TOTAL plan /m2 TOTAL MEAN/M2 N mtAN NAhGF TAAOh
! 0.019 0.003 0.001S 0.0005 ,
PHYLUM WE ut.W T i m t A
- 3. 0.4 0.- 2. 0.79 es = I H. SP.
S.573 0.796 1.1995 0.1599 PNVLUM ANNDLIpA CLASS PobVCHALTA tA41LV AMPMANETIHAE 2. 0.79
).
A mP H IC T t.15 GDr4N t.N I u.4 0.- u.3w ott,1=%A n&CutATA - - - -
-1. u.1 0.- 1 tam!LV A W F % I C OI. l p A t
- 2. 0.79 y FAntbv AutNjCnLA CNl5fATA ANAhtLbipat --- - ---
4 0.e 0.- -- w 1. 0.1 0.- 1. 0.JW l A W A ht LI. A BWICULON D FAulLV C AP ITt Lt.!D At' 0- I. 0.Av
- SCVPHoewoCTuf. PLATVPROCTuS --1.--- 0.1 FAMILV 649trin&F S. l.g6 uAMPHISA SahCHINEA 6 0.9 0.- -
tAMIbv GbvCEWilak -- - 5 2.04 GLVfLMA AMtWICANA 13. 1.9 0.- fAMILV GHNIADIDAE ). 6LVCIND$ hP. ~
-).- 0.4 0.- 1.12 F a m i g.V Lu=uwahtheIDAE l.II LugHw!NtWis SP. 4. 0.6 0.- I.
padlLV mAGtLO=SpAE
= ..L L Ln = A PF TT I M ON E' A E 2. 0.3 0.- 1. 0.49
=ALuANIDat iAm!LV A n oT x t.i. A nCo6A -12. i.7 0.- 4 l.So y'_ _ '
HwahCntua5VCHis AMtHICANA 12. 1.7 0.- 4 1.7o C L V = f u r ti. A TupuuaTA 20. 2.9 0.- 18 6.72 tAalLV h e.w t. l u a t., --- - - -
- 47. 6.1 0.- 25 9.01 L a t 0 4 t h t. l s Cul.V t.M I i ~ ;_,
Ntull5 F Al.5 A 20 2.9 0.= 16. S.9h 0.= 3 1.85 c .2,
= > w e. l f, buCCl=>A - 1 1.0 tAdlLV HNUPHihAt 0.69 6 0.9 0.- 2 ~~
ulHPAida COPHtA owuPwth =thububa - - 16 J.3 0.- 15. S.62 ' C-F e d i t. V qWHINIIDAL c
- 9 5.3 0.= 6 2.21 .
H A P L 6SCOLUPl.05 NUHUSTUS c: - wal>> Ht th hP. l. 0.1 0.- 1. 0.3u ,- n. s C ot,. iv Lo.s w o e w n ll. 1.6 u.= 7. J.64 4- o ,
- t A m II.V P A t* A h ie l D A t A p l C lut. A PHIthl4 A h - - - SL. 1.6 0.- u. 2.W4 -
g _] J t A M i l.1 PH V I.LiluilC f D AL trenNE HFTtWOPouA 13. l.9 0.- 13. 4.91 h..
'J'~
t o o l s. A SA6Guluta 6. 0.9 0.- 6, 2.47 c: - 6 A r i t. V S A M. Lt. l D A L 0
- 7. 1.0 0.- 3 I.48 s a nt t.t. A a l C a oP T H a t.* A
$A.eILV st heubloat u .. a li . $W. 3 u.4 0.- 3. 1.1J
,famity selo InAt
.w.._._,.. t......). 2. 0.. 0..
- g. 0.76
Table 15 - 2 . (Cont.) COthtl.L p t T C A L. t & L Dis Y g He PieMT FOM iINST ouANThe HAsl= = 4 13C et s u t.t. 4JvakALL fL4eMjbA Pout W COhPCHATIon vi N f e4M I Cl}M h JNI { { %{ N h(f tadt STUDI AT Chf5TAL k!VLH P u . t.4 PLANT
---- ---hughtp 06 I n D I v I nta A l.6 ------ = =
---=*=*PtH $UuAWE MtTIM*====- -= = = ul f WEICHT==== ----DNY allGHT-----
N mLAN k & h G t' STD t e t. V Tu T AI. PLAN /m2 TOTAL MkAN/M2 TAans PAHAPHBONu$PlO PINNATA 10. l.4 0.- 4 1.6% POLIDown uth1TLk! 2 0.3 0.- 1. 0.49 , 0.1 0.- 4 l.50 PMIO*en%PIO Ntitwi)HMANCHIA 5. bCult i.t P l 5 SuilAMATA 1. u.1 0.- 1. O.3W F AM le.V S VI.L l u A t 5 11.1.I 3 3P. 21 3.0 0.- 21. 1.94 FAmlLV T t F F.h t l l. ! D A t: PISTA ChlSIATA 35, 5.0 u.- 10 3.42
- l. 0.1 0.- 1. O.sd Pl6TA P AI.= A T A u sa l a . SP. 2. u.) 0.- 2. 0.16 meshLu6C A
[ gj PHybug C f. A 5 5 A M P d i fe L U.e 4 0.011 0.002 0.0049 0.0007 1 rAmlLt ACAp6THuCHITumIDAE W AC 4% twoCn t ress. A P v Ga At A - 1. 0.6 0.- 1 C.dk O 46.3%) 6.622 30.8268 4.40lb CLASS MlvAl.vl4 FamlLT LUCINIDAL Ceibanl A be. - 8. 0.6 0.- 8. 0.)b F an ti.Y LVis4 S i lD A t
- 6.yunsIA estaLINA 4. 0.6 0.- 1 0.51 FAulLY 4WTILibat - - - -
AmVGuatug FAWVMIue 4 0.6 0.- 9 1.1) F A n t t. f nS T h t i v a t: CHan ibfHta WlhGINICA --- 44 J.0 0.- 84 3.29 4 0.6 0.- 4 l.Sl H5The A t'aut hTH IS , FAm!LY s t. a t t i i n t. i COOF 4%28enu % 0uun has? t e 60= D . LA6T COut. 1 86 B L A kCe4 uAE 452000900100 (.
.n a n ragu.aamt Cobe 452000h$0u40
- l. 0.1 0.= 1. 0.18
- 6. u.1 0.- 4 1.40 CuminGBA Ce*AHCT AT A - - - - - - -
StatLP PuMFICHA ). 0.4 0.- 2. 0.39
- tAntLV SilLt h t uaf.
( m s t r. u l no.e 2. 0.3 0.- 1. 0.49
> A a ll.Y 161.LINIDAL Y t t.l. I N A SP. 9 l.) 0.- 3. 1.25
>AglLg w t.est w t u at. -- -- -- --
C H l H *d t C A liC t l.L A T A 3. 0.4 0.- 1. 0.53
* :4tHCtNAMIA CAMPtCHIEN515 4 u.6 0.- 2. 0.79 Cl. A sh cANTunpoua 130.812 18.696 115.4420 16.4911
> A u l t. y ACT60Civipat.
Ar.Ti oC I N A C A e4 41. l f u b A T A 2 u.) 0.- J. 0.16 FAalty .e A g l e .t. I n a t. -- n a p t eeot A 5p. 2. O.3 0.- 1. 0.49 FamILv C u t v i b'il. l D A L ru t p l e ** t. A sal. A = A 33, 1.3 0.- 33. IJ.41 6 A M i t. f a t t,d H.h *e I le A F
- u.8 0.- 1. u.sp
> t o .ce s. e roni+ 4 A 1.
t Aa ls.e t. A b s A w t u A L
+4AoAwfus vint3 6 u.9 0.- 3. l.Jn PHILo* Awlapovoha 6.4 91 0.919 2.23 % 0.4195 (I.453 ( wii% t Art a
Table B-2. (Cont.) Cut h t Lt. atTCalt & t t' u t NFPokT tha Flh5T Guapite na514 - esisCnawCe venfuel tLumlua P3=tw CDwerswaflus utthaLL Co=*uwlTV SThuCTbwt STUDV si CarstaL hivtw Poetu PLauf
--------huante OF lhb!VIOual6---=====
------Ptk Suuakt heftd------ ==--eET utlCnT---- ----Day selCHT-----
N plan kalGt STO u t. y total pla4/m2 total utam/m2 landh sueCta55 CIWMIPF ul a t a a l l. n a t. 4 41 u s t M a l. a m o.% $P. 3 0.4 0.- 5. l.15 5HMCLas% M a t.s CHs TW a C a Owotu Cu= art a usto. Nr. 8.- U.S 0.- 1 v.le FaulLt una5ffL! bat ustD. SPP. 3. 0.1 0.- 1. 0.lr odot w TagaloaCta - -
, SununurW DinONHPnuba untb. .s P . 1 u.1 0.- 1. Q.34 7 ISuPopa - - - - - - -
ttwnt w tw t aplLg aminualual i uulu. Sr. 3. 0.1 0.- 1 0.38 u taalbv Ibatelual - "" 041D. 59 1. b.I 0.- 1 0.35 neDtk anPulPopa tantos awethlectuat , uglD. SPP. 6 0.9 0.- 2. O.wo - l I FaulLi apelTHalDaE
- unto. >PP. -14 J.O 0.- 10 3.10 -
taelty anwiuas d%30 SPP. 6 0.9 0.- 5 3.ub Faalbs ComvPntloah umlu. SPe. 3. 0.4 0- 3. 3.13 tantLv mit.lTIDat u=In. AP. 2. O.3 9.- 2. 0.16 -. Owlet h btCaPous panjLy a t erit t oa t ALPHLub Htilhadh&LLl6 -
-- l . - Q.4 0.= 1 0.4m u.
tantLt caLLlamaS51Dat uPoGtnia at t iml5 4 0.6 0.- 4 1.Sl
~~
faalt Pauuminal PaGuwus SPP. 2. u.3 0.- 2 0.76 }{ T- 7 taulLV P g.%oTMF win at ,- ,- Pl==laa 6e. -
- 2. O.3 0.- 2. W.lt i: -7 -
FantLv PostbalpaE g Cat.LikeCTts SP. 2. 0.3 0.- 2. 0.76 ciLCCi F a u l t.y sawtplnat - y etwspai.netus h>Petssus 12. 1.7 c.- 12, 4.54
"' 9t up asoPt Tenana 1 0.1 0.- 1. u.le
~^
PMfLum tCnt=00LwaaTA 0.020 C.ll? 0.3184 0.0455 u*ID. SP. 8. 3.1 u.- 3. 1.07 pHvLum Cno=4afa
~
Class asciola(ta 6.150 0.019 0.0869 0.n024 unto, sv. 3. e.1 0.- 8. 0.Je (La5% owTelChTHVt5 0.346 0.049 0.0405 0.0115 u.lu. Sr. 4 u.6 0.* 2. 0.1V I O O O
. =
f i
- 2 6
- M 5 _
M - / 3 . t L - h 4 _ TA - T[ NA HL 8 A S Gm 2 UE I QW 't _ Q u - T 3 S VL 9 RA 4 RI DT 0 - F - O .
+T 0 e
- 5 _
- 1
- 2 2 e _
- g 2 _
- / 2 T N .
HA 1 CL 2 I m L u T 5 - CL 5 uA 5 T T - O 0 N - T 9
,e A - 1 L
P ^
~
N V % r t = t u u = - u 6 U = - F = - D U
= - T T X * - S t -W V
- t NI e
61 V t H I t . O [ A u 9 D. t TL A A u '. l l t 2 1 HT i HE 6 OS W A G wPY e I s uN t f nH oA l P oC irsH . a C 5 cT NA T Iu 1 iWi t 4 kt = y t t t OP
. t Op N -
FPu E - tt. T H - 9 i nS p - e r we u . uA u l t h - T t
" h - a t
C ds
- a. u -
t T -
& Cs -
i - h - . T - 4 . S - h 9 4 . Y . T I N 1 L 6 4 e s A T u O e C T
)
t n o C ( t s e
. A H
2 L
- 5 B 1 0
e - l l u uo = @ b T a tSg A t Mw i n a r a I l i i j W W N Y ~
- gd nO tiUF
Table B-2. (Cont.) LONNtlL 4tTCAl.F 6 EDDY M A s t ra - CugTwot HtPhwT enk SEConD 00AkTtR vtNTowl PLUMlbA FUnth COMPONATIOh Ovka4LL CoduuMITT S T H UCi u n t: STUDr AT CHVSTAL WIV1H Pu=LR PLANT
====----abMhtR OF l>DlWIDOAL5--------
-.---..Pik 50.) ARF Mt'Tth------ **--.ET mEICHf --- --~~DNV mLIGHT-----
F a s me h PtA4 HANGE STD DLW TOTAL ptAN/m2 TUT Al. 4t'AN/M2 PHfLU4 l'OM 1 Ft h 4 St.S99 10.320 18.4509 1.1702 P H V lla s. PL A T v Ht LM l**T ut s 0.022 0.004 0.0035 0.0007 UNto. SP. 3. 0.6 0- 2. 0.b9 PHILUM NEMtHTINEA 0.106 0.021 0.0144 0.0029 u' eld. SP. 24 4.h 0.- 16 4.69 Pit t Lu m SIPHNCtlLA 2.508 0.502 0.4014 0.0403 0110. SP. 56, 31.2 0.- 40 16.59 es - _ _ . . - ._ _.
$' *41 L 114 ANNELIDA 13.460 2.292 2.2944 0.4569 s a CLASS POLVCHAt:TA Ln F & # 1 bv - A*PH AHF T I D A E ---- - - --
W AMPHICTLIS GUNta tH I 2. u.4 0.- 2. 0.99
=>LINNA m4CULATA 1. 0.2 0.- 1. 0.45 FAMILt- Aw a t,E Lo l p A t --- - -- - - - --
ANAhELLA [ H I Col.OM 10 3.6 0.= 9. 4.51 SC H I S T O M E R I sn GI)5 WUDOLPHI 2. 0.4 0.= 2 0.99 FAdlLV C API Tt Ll.lD A E --
= f u t um A Sit)$ C Al.l F OR u lf N515 10 J . 's 0.- 6 2.4S 5(..N oPHuCTuS PLATyPa0CTuS 12, 2.4 0.- 11, 4.8)
F AM II.V CINNAfuLIDAL --- --- --- - - - TM4wyx se. 6 l.J 0.- S. 2.17 FAulLY Ell N I C I D A t' M A N P *t V 6 4 h A *Gu l ait: A ---29 Se 0.= 20 W.44 V A u l f, V GLY Ct H ] D AF. GLvCEdA A*t.vlCANA 6 1.2 0.- 2. 1.lu (C FA=ILv 60= l A o i n A t. - - - - --- -
-n. 3 .
GLICI4Dr. SP. 1. 0.J 0.- 1 0.45 > F Am ti.t HLs!OvlDAF -] G v P T ! F, ma t. v l P A LP A - ---- - -- 2 0.4 0.* 8. 0.55 t' A n' I L Y Lil4 Maa l et WL E D A E
'3
~6 LuandlNed!S SP. 1 0.2 0.- 1. 0.45 6
'Ub 6A=IbV aA66Ltr*lDA6 - --
MAGtLuNA Pt TT !etONE AE 1 0.2 0.- 1. 0.45 -3 F AM If,y M Al.D A NID A L Aalolw&Ll.A mHCn64 75 15.0 0.- 55, 22.96 ,i wwAnculoAs CHIS A9LHIC A Ja )J. 6.4 0- 16 1.92 f F A 411.1 **WeIDAE :-- ' L A6 oh t.W 6. I n Cu bu t.w l - - 6 3.2 0.- 6 2.6u -- > htNLis suCCINEA 24 4.8 0.- 12 6.57 Nt Ne l5 SP. 61 13.4 0.- 62 27.20
~
PL A T W ast We I b DumbWlbli 80 4.u 0.- k. 3.46 % ' Hutu. se. *2 1.u 0- 4 1.))
> A m l l.1 endelPH!la46 n.4 u P.* I 6 mt nuto:ia 147 JW.4 0.- 15 16.0b
)
& & a l l.1 ow et t '.1 Il A t H API.usCisL WLOS w a hu silld 7 1.4 0.- ). 1.34 9 9 i
9= Go.
Table 11 :2. (Cont.) CommLLL *tTCatt 6 EDDI $LCohD tail Apf t p l ht.PohT t ost HaslN - CoNTwob t 1,uh l u a Powt H COWPuhATION UutHALL r e sv r u pe l Co*MUNITV STHOCTumt STUDV AT CNf5fAL RIVth Postu FLANT
--------humptw of I re O I V I DU A l.6-= = = == = =
...----Pep SQUAN) METLN-===*- ==**Nt.T uflCHT==== ====OHV m t' I GH T -----
WANGF stb 16V Tilt AL PtAN/N2 TOTAL wkAh/42 TARhN N MLAN NAINLWtl5 $P. II. 2.2 0.= 9 3.m) SCULOPLiiS NishM A 9 1.W 0.= 9. 4.02 t Ag il.V rasvan= Inst ANICIDt A SAILOWI 'J . 1.0 0.= 1. 1.41 t198LV PLCTINANllDAL
- 2. u.4 0.- 1. U.SS PFCitNAHLA 60U1.011 0.136 0.027 0.0339 0.006u PHVLUM SIPUNCHLA Pet V Lll a A se '.t.1,1 U A r.-e F A
- j l. V PHVI.LHDOC]DAE ---
I t.1toNL HtTthoeuon - - - - - 6 1.2 0.* S. 2.17 L3J FANILY POLC)LOCHAETIDAE 12. S.37 Pot'CILOCHALTUS JOHNS 0h! 12 2.4 0.- p FAMILV Pol,V NO I D a t
- 1. 0.- 1. 0.45 HANWti,bly. ACULtATA g.
0.2 l.6 Q.= 4, 2.89 -) FAmlLV 1.t P l u A m t. T H I A COMWLNSALi$ L,Pino ofus 6e. SAntLLIDAt
- 3. ... U.- 2. 0...
2.74 (m -/
' Sa 10 2.0 0= S. (' , d/
C HoNt: Ots N t W I 0.5S ,, S AHe l.b4 MICHoPTHALMA 2. 0.4 0.= 1 0.45 g
.(<
04 o. sP. i, o.2 0.- i.
'9'.~.,
FA*ILV S A 6tl.l. A N I I D A t' 7, 2.b6 6 A hti,1. 4 W l A WHL4.AHi& -18 J.2 0.- g tAMILi SCAbinHeGmtDAL 1. 0.SS f_ d' MV60SCHLtA LONGISLTA 2. 0.4 0.*
; ..]
t Am tl,V 66Heublott ./ UNIO. sv. v. 3H 0.- 7 3.01 ~1 -Q -
& A M ll.Y $Pllb eld AP i, - ?,
- 4. 0.J 0.= 1. U.4S - - 7#,
P H li th8 6bP ! U HP I b MuhW A8eCHI A tAMILY SVLLIDAL 0= 2 0 u9 ._. : L I OGnN t. USSPAN 2. O.4 'l hyl,Llh 6P. 29 S.6 0.= 25 10.WO t.. , ( - _;J tAMILV TtH6MP3,LIDAL 9 1.b 0.= 6 2.6d 7 ~O LuslLLA ALHA
-11. 14.4 0.- 62. 24 9J ,p' '
PihTA CwthTATA --- 6, 2.nl pC' PISTA PAL =ATA 7 1.4 0.- d STweHLush=4 et A R T4 A N A t- d. 1.6 0.= 1. 1.14 W. l.4 0.= 7 J.0S u N i s>. 6e. P u V l.uu Pol.tusC A 0.6b3 0.136 0.3000- 0.0600 Cl, A 66 Ameel towA t Awit.V AC AN THOCHITL)N ID A) A C A N TetelCH 1 f a sN A PVGuAtA 37. l.4 0.= s. 1.HS
& A g i l, t l e CH uoCoe l ton l u A 6.
[ NC WH iCH l ii t1 P A P il.Lij Alis 17 J4 0.- 6 l.44 61.9h2 12.396 40.0944 b.0069 C l. A N s Hlwal.VIA
- 4. A e W I C aw u l u e aa. na l ds.1 4.1 13.4 0.. Sb. JS.in t 4
- ll,V CawolighAt C A w o l l A o t .* A F i s os i n a .. A 14 14,8 o.- 37 17.40
8
# ,j ~ -' '
/ 3 ,> C .
^ f
-}a !-
f h' h_ . Q~ 3,1 i ~ T. t ( - gi { -(7 t c,
- ?
- u w - / 7 - 3
- t. L - N 0 7 TL TA 5 2 NA HF 6 9 A w CM -
ut I J 2 Gu o t. n , N Yl 7 t O P A S C DT 3 5 3 t - O S - T 2 6
- 8 4 1
1
- 2
- M
- / 5 8 9 7 TN HA 1 4 Ct I s S 0 1
E u T. L t 5 6 eA
- T 1 5 4
T - 1 8 9 N - T . A - 5 2 L 2 S P R V t
- - t 9 w 26 e 0 603 37 0 5h l0W 6 965 e l 8 9 S 5u 9
= - - U 7 W 39 1 333 4 744 w 7 3 O - - . . A. 6 5 b. 3 1 4. t. b. w. 0 . b. S. 4. u. u.
P - - D l 0 0 8 4l 2 323 3Sl U4 S32 Q l30 4 S 0 J U Ul n
- - T 1 1 1 1 1 5 h - - S t - h W t ml sT V h h lt . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
D I au 4 2 4 0I 1 7 1S7 723 1 9 17 9 1 491 9 4 2 W 1 12 2 i TL u 2 2I1 2 3 1 2 111 1 t A A Dt 1 d T l wE L oS vA G d Pt i uN lF,n noA - = - - * - - - - - - - - - - - - - - - = - - t w oCh . . . . . . . . . . . . .. .. . . .. . . . . =. . . . a C InsR 0 0 1 000 0 000 U00 00 01 0 0 000 0 0 0 0 0 00 0 C1 T u TwpA F t tap oe mV nP e oo u-L. b Pu t - i T p - W 4 4 6 264 442 2 0 2 4 4 t A S m - h . 6. W. 6 2 $. 6. J. M. 0 9. J. u. O. 2. o. h o . O U U S21 e 6l l l21 UI 2l i O 01 0 J S 1 J 0 0 l U O N i th 'H u.A g t m 1 I BJ t C oU - LI - tC - u - h - . . . . . . . , . . . . . . . . . . . ... . . . . . .. . T - 4 2 2 84 u ) 1 87 1 26 19 364 l 4S1 0 6 S 0 2 1 S 2 S - N S 28 4 3 1 S 169 - S 1 2 1
- 1 -
V - - - T 1 - 1 - u n n - o C A A A r m C - 4 a u 5 A I - 1 L A 9 l l S M 4s N A D AA u 4 m T A 4 i O A UU! T A A TA Ec Uu a C 4 lW L I G A I H Ai E d t AEWI ACA t C EAoA k I A A TA A 5, DC A l HW A H A t l T, t A L ) EI t N V Hw l CuETA A. t UN DluN lpfLN tA k C A l i I I I : t I. A P u C A.a h !wDuS gLPLPt nA u F. lPni t d
. A TE A !tPCt tvFsf CA A N
- FLC DFA 4 Dl sA t r a ni4l ut A A t huuLiLA a hl A d if .>. A t
n I l o .I A nPW A o A. lut0fl aX .DcA I.t uA MCA lPL4! t ml 6 mt O ID b L. u p AW o L al Pt V I. Ll t A 0d h l, EPI *hL i l H p H6 N A i. N HA b C s.u ttA,Lfinn] asnA C lisuSnMli H H Aca a i M i d l Hswt t uePL e TSi ALAI A A A F F w L. u u! LA A A h tCL pPLLLCA I uuV o
.M OuDA wT GOI MPSuA Lbd F p nSl T C l.
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. i V o = A A V lo l.
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& uS vA G W PV i l l N f h M h noA - - - * - - - = - = - - -
l F OC a nSH . . . . . . . . =. . . . . . . . . .*. . =. . . . . C i 0 0 0 0 0 0 0 i 0 0 0 0 0 000 0 00 00 10 00 rT T p TS MA rt t D t. oP aF nV -
) UU w -
L. H P U t - T e - 4 0 4 . 4 6 4 4 4 4 2 2 0 6 62 86 l. t A S m - N 4. J. 4 4. h. 4 e. h U uA 6 1 0 3 3 6 4 0 0 0 u 1 Ol u 0 3 00 i t J 0S h i t m - L $ l sa H w -
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. A H I 4 L L A i aChI A J 4
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- t LwaSI i F % aUF. w n
l DA . - t. t A h P N A 4 C l I l A aI t mA t T La o IHD .iA I f u D O S A E t A iH D i T DMT wN t Pp t. l H Oh P O.t s uf C F I Pst % m I N nI . H' .A .D .I H .T I N I N 6 oA a8 V. iA uSi P d P i ( PN$ urff . o . t .t . PT PDeIPPPO .T .A ,4 t A HNI 4t wDoI M N . t N 4 CA e PNPA fPA P o otL. P I PI eE PoPCPI PI Pl eo : L, AI PPl O. 4JA A NGsS u PA vv t A. l' I S0Snl sHSP aPSPSW sTS w S U 6 L h L S O P,lSssl La1 b IINAA.l H1 l h 4 i H i P M u
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M C A. 4 N u oo n DP D D o u u D n iuC 4 e i Ht G P aw I H l h A, A A Ml wl s pep O P iGl 4 V fa i, V IN mA V 4 t N V . Vs.%V uY u) 4 v 1 I B l l 1 t N U V. L L L V. Py p I M T I ) A e f A a I L T NHol t utg isaI Y, ,,LOl l a 1 1 H C 5LM S
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t l PmbPP l M A. dla n uM u wM M M
- M m u g MM M m M
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A.l A C6 1C t M l M U t A A t A A A A A A A a EA A a A A A l e- i pt F Dt t F F F F P t DF F F P F t N H 4 S en w P b lH N amM j T t Uf o o O a %m A t 4 HE S N T H v f
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Table B-2. (Cont.) OmhtLL a t. f C 8 L F 6 6 otty HASIe - C ON T + 11- htPORT toa stComo unaptew v t' m t ow l Slow 104 Postk COMPowaTIO= HW6d al L Commu41ff SThbtfunt STUDr af ChV5Tal. kivfW P0at R PLauf
--------humbtp OF INDIWIhungs--------
==-----Peu S a a a h *: atTeh------ =====tf otIGHT---- ----DNr mEIGHT-----
tauqN N atak k&NGt STD Ltv TO T a l, Ntah/M2 Tufat " fan /m2 UNID. $P. 1. 0.2 0.- 1 0.4% F a* Il y PtNattuaF Praa*us sp. 3. 0.6 0.- 2. 0.h9 eam3L FINmusethinat Pt.4atta SP. 5 8.0 0- 3 l.41 tanlLv Fwot'e s3 l va t 4*HinentFw s1==tTwICUS 9 1.8 0.- k. 8.a9 taagty sa%ruloat tuMVPahoPfua (*t PWFSSUS 68 11.6 0.- 45 19.45 htnPaNoPt PACmawus 5 l.u 0.- 1 l.41
%6hPadopt Itnada 18 7.6 0.= 16 4.73 Fw nthPanort SP. -- -- - - -
-92. 10.4 6.- 49 J9.e6
, P a r. 0 P t. 0 5 M t.h 65 T I I 1. 0.2 0.- 1. 0.45 g < paNopeus DCCIntNTAL15 S. 1.0 0.- 4 1.13 ui witHdorth0Ptu6 Hawal6tl- 4 Gm 0.- 4 l.39
'4 uulb. SP. W6 ii.J 0.- 39 16.9u PHILua tCultoothunga 16.216 3.243 6.0333 - -1.2147 trwtu. SP. 74. 14.8 0- 31 19.58 PHVIu* CH+mDATA - - CLANS 45tiotaCLA 29.011 S.e02 3.215) 0.6435 ustu. sp. 37 3.4 0.- 16 15.99 CLAN 6 obit!CHinWtb 5.414 1.095 1.0495 - 0.2099 UNID. SP. 20 S.6 2.- 12. 4.25 g~1Cm{) (? b z zz s-. L_
' - ~*
e m O O O
Table 15-2. (Cont.) LeshhrLL '.t T C A l.F 4 EDD1 g waste - re s '. t w e e t, e t Pilw i t s'k 5FConD 441 Awit u U V 6 6 A l,L Vtmidhi & LUN i t*A Puat M Clik PUN A T I Dd C D 4 mi1 N I T Y S T h isC T u r t. S itiD V AT CWV5tAL HIVth Puotk PLANT
-------- h u M 44 t W (b$ ] agl1 l y { {)ll A (g e. . .....
==-----PtH Suil AWF atTfH------ ----=FT ut!GHT---- ----OHV nFICMT-----
N a t a re F A %F STU LFV TOTAL stAN/M2 TuTAL
- TAN /"2 T a v o.
TOTAL 75b0 Sis.u 26d.- 971. 2S4.50 457.627 St.505 10% 1A07 24.0320 ev . t vi CC ei C',._ t kfC
- p. . s b
en b uur 4r M
= .a M
W
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2 4 K4 O O 4 7 Oy e
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- O s O
a mJ C 4 4 O ** Q JV O 40 4 9 O O O tt' t > 0 W 3 e e 8 O O t 9 N e3 0 % O
>E O 88t Z 1 O
- Js e e
== a O O tes B
De a de ae >= -e B be 3 *e
>= 9 0 O O 2 9 Se e e 4 9 O 8"i
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a 5 0 g em 3 3 p 3 e seg A e e 3 sim m em oa3 g A eO 9 3 9 3 3 e e s; #l due at * *=' em .e M e @ at N me .= mm *t 8't *ut m *A 99 m =* 9 e e e e a e o o e e o e e e e e e e e e O g e e e e e e e a e eO O O O O O O .e .e N O O 4 .= e m == O O C == Ne 3J C C O O e= Z 9 9 A
** O 2
> 0 w 2 == to te e e e e e e e o e e o se
.O. 3
.a .es 4 3 am e e we e
.e e
em e M o e est ese e e m e a o e p.e seg esg 4e ,e=o aug ag D == a > .3 s 4 4 C ^4 s >= == aw J 'O E D 4 5 14> == 7 2
- C 1 61 CC4 0 B 6 0 0 e I e 9 0 e s e a B ee e t e e a 0 8 I B B s V & AE e o e e e e e e e e e e e e o e e o e o e e e e e e e e V ** O O O O O O O O O O O OOO OQOO OO O3 OO O O O
- J r=
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- e e
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= w m m a
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7 f6 3 == A a 4 a4 : 2
=
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== J == == 3 V = V == W J-e** 1 4 C > d ; I O 1 4 0 4 .x 4 4 2 1 4 J 2V4 4 4 E >= 0 J 2 == = 3 J 4 2 Ja 2 .al =>C 3 V >=
- V a= 4 'k
.O J7 1 4 3 *=
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=V$ =3
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- a= 1 4 L to I EJf4 == A a 1 A1V == 4 V 2 el
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== I !4 4 4
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4 8 T A #4 & /4 4 6 14 2 FA** 8 J 'J T J*=4 X T
'J 1 =* 2 C4 s 2 E V2 O4 4'
44 TJ14 == = = = .J 3 : =4 04 1 I E 44 A .' f == 2 A 14 20*w s K" IO A I e 4 k
- L * %4 7 4 ===8 & V O V n= 4 TU*J1 7 47 6.* V* I #==*= *O4 Y ; 7%'==1=141 2 I 1 O F "., ==2L ** 2 1 == z 1 V & '
4 O# 7 ; 6> 1 1 a .3 VV r= J = N / 4 ** O == . es .J 4 4 > W J == 4 a= 4 1. 4 1= 2
- A ! V = 1 l WF 1 F Z J me . ** 2 a= 1 se 3. = I4 m34 m .,y a = m4 w4 1 4>d
- 4 J m =2 m e Q>1= = 2= * *
- f* *
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. w . w w . *
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b 4 e 4 I T TV r = 2 a s I-B=59
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==
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O2 4 C E Q 2 > .3 *
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- M #
W G 9.e d e
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8 N 6 W @ O G% e 9 9 t'* be 2 O
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e en e
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6 D= T O
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2 > m 2 2 @ ea ? M a 9 0 4 ? 2 2 3 e a e 3 .a O 2 ? 2 2 see we a* e Z 9 4 s 0 0 3 9 ** * * * * *
- ret at seg == 4 est
- e e o e e o e e e e e 4 e e e e e e o e o e e
.o 3 *, == C O O O O 3 C O O P A 6 8 O O OCO O O O O e ee 2 9 6 4 4 8 2
> 9 W Z ao 44 he o o e e e o e o e o e o e e o e o e e e e
> 2 .2 m en p g .= a= == == -= ce c == c o 0.e e 4 m se ==e== me == em Q t= .3 3 6 4 4 T 9.* ==Ca 2 .4 4 CA >4 0 2 1 ze == 02 B e e e 4 e e e OC4 8 9 0 e 8 g e e e a e e a02 X 0 e *
- e o e e e o e e e e e e o e e e J 4OV 2 V. 2
- e O 4 me Q OOC C C C O O O O O O O O C O o C O y e. L Se a e= 1 E4 k4 s : m C1 T 1
- w e
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- en == we ,e 9 == == es e W ** an 4 6= 3 4 es em me .= .= se est o e e e o
*
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*U S
- 0 e e e e e o e e e o e o e e
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N = -e se as en en se e 4 en se t% en se == en s'9 C N # be $ == == trl 0 2 en me 1 De D=
=*
2 O I i 3- a' w L 4 on Z 4 U /
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^ == 0 O.
p 4 2 4 T 4 e 13 '6 3 2 m 1 w 4 4 L e O 4 as 2 2
- A g D 7 4 4 4 a L 1 1 m b'8 O I *e 4 4 I
. O=* al7.e'd 14 g -
4 = :n 4e4 a 4 tea t, ; .O 3 4 I 4 4 4 . 1 4 4 4 J ar y at 4 0 24 4 4 3 as =e. =1== O=
-eO1 == 0 *4 . I J =g1e===3 =,=4
; e e- C / s _" -
Q J- .! -eT e C.-a 1 as o J Q ; O es we 4 se==== * = = = = 3 1.;.= 0t 2 1 == 4
- e. e 3 at 04I2 2 . =1A == 4 = o4 e = A y .e c w w 4 ItY z r - W z 4 er g= > 4 as / 4 1 a - O e *O J1 014 a I JE 4 ? v4k 1 7 a 1 *= a 3 I a m 5 0 - 1LJ%.1a 1?e CO==# 4 4 0 1 4
*I 4 A4 04 1 == 0 W -o J h= 4JT44 2 2 e a2 . =e 4 ==>J.
!9 J 1 2 **
= 04 -4 O 4. I J / 4
- 7 A 1 1 /. 2 / 2A -
J 1L 1 4 ! JO1 2 1 J 7 2 4 1 2 2 m Q == 4 Q 4 2 m =o > e C .es F 'i a 14 74 1 4 2 eT*= *
,4 4
I
#4#1 F
** A*=P as 4 03 v"
J e-2 C Z > b - >J A J 'A F7 O ZC V. hm Oa = = 2= > 21 1! T ==4LT= E #4 04 == 1 J 4 1 == 1 p.= V 4 F 0 01 4 e4 0 o4 4 &
==2V T
= 1 4
= ea * *E 4
- 2 * * *O A
-l L Z
T 2 -=e
> I > af Y E => >*
J ** 3 as & J > > ar >Jww>Y U== C w '#1 J 4mI e 4 0-
>4 2
m=> 6.= mr I /. t= 0 > 4 = *- e
~ > 's>J ** .*J >= g 4 .J 1 .Je L .4* 9 E 2/J ; J a J J J 4 0 JV411 2 J V .J B
- == -e =
- == J J J at y y * = ,3 J J.e 4 ==
T 3 7 4yA. 4 Y a 4 2 9
==
2 I
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I A e
- 6 e 'A 4 2
A 2 2 f A 4
- A t 34 3 L 2 T O 2
O ? 0 e.m
= ' "
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I' t;s. , [ i ) .' i , ( . * [' {'
} Q _s - " '
e O N 9 E
& 4 % l
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to J De 4 i T N 3 4 IJ O O 4 X OE * *
= 4 ee O O l' s Ana O
- O Jr > J C 24 O e U C D*
- N
- 9 3 O e M e e= "9 a g e e e O O t
9 N 8 I e% *
- s2 QD @
E at ** O Om *
- se a O O laa B
l* kJ J B 4 O == 6 De @ 2 ve eO N d 2 8 De e e 4 e se O
=J A
tz > m 0 0 w == N ed ** 4 > d't 2 r= N P "9 4 4 s 8 0 J e fm a r= w r= 9 # ** A e d == 7 @ O 9 9 e o e o e e e e e e o e o e e 1 0 0 C == == *C (% C O O O == m 3 ** a5 O I e e. 2 0 0 4 4 8 2
> 0 a 2 e* 4b me ga 4a e e o e e e e e o e o e e o e C em en E m e nN re em N en we me w 9 N n' en N C >= J O .= .*
W *E as CW X De me 2 4 J OM > 4 0 2 1 se == =2 604 Z OO4 8 0 9 0 0 8 8 9 0 0 0 9 0 8 8
; OV a v, a e o e e e e e e e e e o e e 4 V == 0 O OO OO O O OO3OO O O Ve D* Z
>L 34 ss a Oe C1 5 1 Om 9
*OC E 6 4113 6 9 a to 1 0 O e me eut 3 **
- 4 == ? ? @ 9 O r*
4 4 et) S 6 E
- e e e e o e e e e e e o e e 2 0 3 e 4 =* = NO == 3 O 3 OOOOO at 3 J == 'an X 0 M C 2 E 6 &
V =3 9 4 em 0
*U e 3 0 2 6 e e e e e o e e e e o e e e e to O r= 3 eN mN ee e j oe e4em me e I 4 $ E a m m N j l
to ) se E 5 2 5 O M , U C 4 ft > i 3 =E == 4 -O l 4 M M T C3 i O O M t= w as U ' W" M e= 2 EU me 3 4 K eue l fx i 3 U 'd LS 4 De R 4 W as A a= r as ' W *% 4 I A
.L. O 4 3 4 : i,a3 7 6 2 e O3 0 g O . as x me &4 M M == i 's J 2 >4 at e # t J4 e 7 = p, A at '
O.eMe A 'a 1 "e, er
>10124 iO e Z eM COh 41 w M O J == 11 > F=1 > C 4 'aJ r%
- C 4 2 v. A & 44 tr o C 41'a M .2p.,1I=
- 4 41 2
- k * *
- V a, 1 D= 0 4 E T at 1e V e 's C114 21 I1 U 1>JA: 0 == 2 f. /. 2 4 O or F 2 001M a w'2 4h 4 2 == J 4 24 1 J4 0 = =a 2 i er 4 2 2! O HI e ZO12 1 4 y Cm + e1=1Oe1 4 4 2
- e *E U *
- I 1 7 4 == at O F me = 1 1I O C* O O == 0 V 1 O JZ F == 2 T 2 0>=** = = = X 'a =
N 4 > ee >d *= 4 a, > 'a 2 3* == >r>! e a == F T 2 O t= 2 g *
- 22* U3 I#3 M 0 .J Z yJ 1.J.1 1 J= & I .J.1 4 et
== =
- J. e.
e . U= r r r y r y e- 4 4 4 er 4 4 4 Q R i.se e a e e 6 6 T I M er i = = in
= I a 44
- c k, - - = as a -1 i m k 4 I a IO 1 h I-B=61
' 3 l I i b.
mp :- 0 _ 7 $ [ __ A - , c(_ ('- E-T :. . .t,u 2 0
- 4 6 W - / 2 t L - N 5 i L TA WA HE 0 lA N Cm 6 !
iwv t O m D 0 h YL 2 o aA W C T 6 t D. O S - T 3
=
=
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- m 1
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=
T 6 FL 2 s A 0
- i. T T - O 7 N T 1 A -
L P R V t = . 6 2 e = - b 4 o = - P h 7
= .-
= t1 2 e = - 5 t = s t = t hi 61 I Oh L t. .
D I Af u 4 D TL 8 t aA ts it hT I k t
&
- oS pY WA G l ll N fl F'UiCCw > hi 5k i
e
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- e. uD N -
L. h Pu i T k - k . 6 r A S u . e r
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LT - F ( - u - p - . T - 6 S - N .- 2 1 Y T I M u L a A a T u n C I
)
t n o C . ( t, r p A
. H C
2 N
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1 p
= I e N u M
e l Ir P b f t SN 3
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a e t e O
% e % r , w W ~
HlM. i @ or t
% f-g wr s f s g . + r 1 i l' I ,? j i
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f a_ / lb s [. t '. I II t 0 9 N G E a 6 % e N e m a wJ b 2 m m C @ 9 kJ M4 e O O m m 24 Zm N O O O N 4 3 Og e e e e e 34 m O O O O O O2 & O E O
& >J m 34 @ N m 9 N K QH % 4 N & 9 e GO e = O @ W D H m O O O m e e e o e e 9 m O O O . =
8 D N D E 9 % e e N S
- H I N = 0 O N Z4 N O O = m
- g. e e o e o ma a O O O m a
B H AJ E 4 7 O N O e e> N 2 m 9 m H I O M G O e @ 2 t e e o e o e 4 8 4 O O O O J 2 > m 8 9 . 7 O e A me SS = O @ em ** SW Am *AO P *& *
- 8 8 2 = %
- W S w e2 9 m @ AP @ QWA De 3 9m 3 e 2 n O 9 8 e a e o e o e o e o e a e e o e e e o e e e e e e e A 9 8 C *
- 4 O mo N D m = O 3m m am m QW OOm O m3 =
9 ew a m X 0 8 4 W G Z m 0 4 Em @H w 04 J. e e o e e o e a e e e o e o e o e o e o e e e e e e 3 m 4 3 e m 9 = &w en m N = m e newA *N N*N N WN w J NJ O m N m a e 4 4 CJ Ek = 2 n J OM 3 4 0 11> m: 3 4 04X 004 0 0 0 8 8 e 9 9 8 8 8 0 0 9 8 8 8 9 8 9 0 0 0 8 9 9
- hOu I Wa e e o e e e e e o e e o e e e e e o e e o e a e e e 4 W m O O O O GO OC O O O 00 0000 OO 000 O OO O Ok M 4 MZ 34 66 s Cm 01 5 1 3 > e 4 00 MR JX 13 4 0 J H 2 0 3 3 3 N ON M@ O N % fe 49 3 4 94 313 @ @@ O
- 4 4 W 0 2 e e e o e o e o e a e o e e o e e o e o e e a e e e 2 3 3 0 4 3 O 9 O NO m3 m a C 37 0500 09 330 3 m 3 -
2 me 2 8 4 0 X X 9 5 V 03 0 Jw 0
*U e 3 8 2 9 e
- e e e e e e 9 e e * * * *
- a e e e e e e o e e H 9 e 9 e m om dN d @ m Np em Nm Weg N M N c n . , m. m . M N. N
=H 2
X X C We U 4 em = =9 . = 44 2 4 Z IV 4 M = 1 JC U J J *z m > 4 0 31 J K / / C sm 4 W r 2 3 Ok 4 6 5 Z *
- % TE 44 J 4 M 4 4 I b== A e A4 O Ju d 2 2 9 J 4 2 4 0 I y 4 kWJW4 J1 w 4A 1 OW 4 4 '4 W O
- C e
# C44 0004 OWQ4 ~ V= 4 m OiA Z-2 . 61.
O a =JCVL*=UWWJe=Op 4 I 2 M2 J4 0
- r=O4 44 O I W Um= FJ 24 2C 2 =w0 2Ved e 4 1: 22107204 Om
= uGJZ=Jt% Com m 2%= >4 2G : 3~1Az4 ==A=x e*n 2 24J=I A U-42 7 0 4A2Ju a =64 =O = q ; T ; ;
V = e 4 e
- 4 4 1 m skh CO wd J .1 24 J4 =4 71 eX X ? JA4=m rww E 1 d i 4 1 WT 4 414 T41 = d 2 = 4U = 4 CJCW4 4# 114 403 TZ
=C=Oh zwa J o"JJEe eE O 2
J 4 z J /. A m 2 W J4 04 X
?
2 '. JO14&TA>4 3>4 rOO>J2 4 : 4 10TJ a =E*444 2 7% =2 UmdL.4 721 r: 4 04 0 7 C 2 4
- I e
> O w e 2
U 2 2= mI4 JU m o = RUCIATU6 E aE
- V2 m l 1 y A 02
===
*O4==I CCJ2Jm : 1-12=m
., =,= 11 p :
N, - - wm w- == sw J . x = > 1 > 2 ~4 1=0 . 11 = E T 4
- I I 1
- 2 J>i>2U>:4 Uwd>Jm 4 > =2 >4 44 23 *T 5 4 4V>4 a w T e
- 1 a 1
- J 1
& 3
=2 e 2 TJK -J4AJKAJK 4 1= = m -JC21
= =J4 K J2 M
=
23JOOJZ E / J 1 _= 4d
= - = =
JJG
=
y 1 E E E E I 1 1 K 1 1 ? ?
. - 4 4 4 4 4 4 4 4 4 4 4 4 4
- = g nr. - * . . . . . x .c 2 _
=-
t_ 3_ _5 _ a m .'* A E .:^ _ m J a J _J m J4
>J d e 4 I I T T TV
- - - 1 1 1 1 1 I=B-63
$ I )
l l , f ( ,' i ,,
..s)
- t. e. >L a a
4 O N O E # d a $ % e O e4 P* 6J G Z ** P* O t= .3 >= es N N
.E 4 1 (ad O
- e
- e K 0K @ 8'9 Oe se O N
0m W 3 m o a >3 e @ N ee Z 4 S 8'9 S T C De F* 8 d to 8 O # N 8 c= O e
- e
$ a @
0 O se f se 4 9 N 0 K .=
- d ps2 e
O'"> e e e Z4 e e e g ,,,
- O N
= a 9 a
3 tm
.e3 2 N B as e a E
@ N O >* W @
se to 9 O e
- e 2 4 > "o N as 4 O N a'e
.3 N
.1 3 3
@ s o 4 @ f'= r= a= e e S == @ e
= 0 t a; 9 @ *4 # == e m 4 cm mP 4 s me me eg 9 4 w me w on O &A N S e 4 J o e e e e o e o e e e e e e e e 3 6 9 e e e e o e = c 8 0 C C ** == O o ee CN O f* O N N @A N c o == ==
1 a= e= 0 8 e= m Z 0 0 # m 8 A
> $ W 2 == *C e e o e e e e e o e e e e o e a
,e to Oz J 0=. e o api .e o
g e
.e g e. g .e o p.= ,e sie p m g e em 3 ** 4 5 N T wS O
== N O fe .J *et
- 4 4 C. a 1 ee ao E
- J C# 3 4 J c T 1m e= T 2 3 4 8 0 0 C74 0 0 0 9 9 0 4 O 9 0 8 0 0 4 5 3 0 9 le C2 X e .2.e e e e *
- e e e e e e o e e e e A M2 e e e o e o
.a a OV 4 V == 0 O OO OOo OO O C o o o oo o o J o o C
.e V> t= 3
> a34 am O 6 ') 4 O1 0 3 1 5 m a O e CQ S 0 Pe J3 13 s e J B ea ma e e 4m 9 e e't N ce N N d'4 N
- m9 O N
- O B f4 e
o e e a e o e e o e e e * *
- 4 4 A E e 2 e o e e e e 3 O -e O "* O se A 3 =o O O *e Q 3 d 3 3 0 4 3 *e 33 Q == 4 5 **
# = as 2 0 ai 4 3 2 1 0 5 y V 2; I 4> e t
*V 4 L l Z e e e e e e e an o e e o e e e e o e e e o L e e v 0
N e set as es r= e, mee A se e es e w o .e N e e ==
>= 0 me *is e9 4 0 E in m
M 2 ao
**he l E w 7 O T C 3 y 0
V t= A as to 4 .J 4 0 la @ an e ind 4 at 4 4 4 e as 4 4 .e; O == 1P U 2 F 4 == ==
# 2 e== 3 2re J
** F O4 at C K 2 O J& - J == n -2O.e =O - 3== 6- .Ce 3 e.* g T e 4 4 1 43 ! ? ** O1 ' L .2 Y D C4== e OV 4 0 3 A
- O' *4 2 C 2 1 4 7 a e 2
^ a 2 C O 4'e ".J 4 ao e b 1 5 4J O == E ; O g e m"e 6 - e. a 3 I O2 == 4 A r,,; Q . s o. W L '. A y C 4 e == * * - A A = .; X 's e 1. .J e 4 e-
- V T7 3 e 4 e C ar = 4 4 4 1 !
y m i d 4 z 0. I 0 4 & J04 3 - 4 $44 J1h C I 4 Cb O ! 1 *4 $ 3 34 ~ O e L == , 3 I == 0 6= = = . -e J 4-
; .=.= g J g . x y ,,= ; _r 7 g J at == 1 2 e . J /, 2 9
== y -. s e a- . g - g -
* *44 == a
,s ==F 0 4 *= I J - **s 2 s6. ;
Q -* T O C# J=*C11eE4 ei =23 413 4 1 1L I T K 12 =e O 2 - ae = 14 ==
.= 2'".: 1 A .J 4==
- La 3
/.
4 : 6 y . 1 4 -=J 4 -e 1 I ** A A2 e
* ,J J'm O C
J e 34 O V V e as 1 e m == e. e*. V. .A T# ; =L4 be >0 / .C I 4 a a; 7 J3
. *401 24 p17I 4 O *e & le V1 .=7 'Ig 3
- == I 2 == c2 Y ZJf1 4 =a e 9. .34 as 23 v 2 g e ea 2 m = y me 3 e ; f . f 4gf='=
3
- =.; JV 22 .',,
==e- ==Cy d 2 e J e.' W JC 6 T,== z T 'a O I # Y .e.
e- *' == 2 J e-44 . 2 d r ** 4 f e
** f X .3== C / 7 ea 3 JT 4 e==
Y4
- 2 A>4
- 2
- 1 / D= 4 *I- J*<*- J #' * . 7 =
F >W 8- 4 ma > 2 m m == 3 T p= .J 1 as U w 4 *a em 4 % ~. 4 J fa
- JT 4 :
- 4 OJ1-7 3 4 7 3 .3 e J==a'=
== r
,,2J U
=
.3==
J. v 0 .J Z . S 4 e== g- - .* g ** - - 'f V .= J4 f a.1 7 1 a J. 3 M TY .J J 1 ** !
; e ag .o K X 2 T T 3 3 5 f 8 e
3 e g 8 - 8 4 at C4 4 4 4 at e e g g g e as d /A e I AE I Z
- a S *
- e w W 4 F # 4h W a m 6 4 4 4 A 3A : /
R ; T an : A A
.J J= = = 2= J=
,_e - e- : . J -
* =J e=
I I " 2 O y= y y IO yu e a. 4 ;a gy 1 1 ,-, f D = U t i 4 e 4 4 e e e o o e o e o e e s ) ) ' > ) 1 I-B-64
Table B-2. (Cont.) CommeLL = > TC al.F G LDDy M A s l es . CH4Thob strin*T Fow THlhD QuakTtR vthTUNI fLuklDA Puet W CON PON ATItim taVLRALL Cn==uas!TT STHuCiuhl 5T001 AT CHYSTAL Nivtw PuotA PLANT
-. -===.aOmetR OF INDIVIDUALS.======= . ...-.--FLM SuuaWE atita------ ==--=FT uEIGHT==== ====Dat hklGHT*=*==
I440g M Mt14 NANGE STD OLV TUTAL MEAN/M2 TOTAL mEAh/m2
,. CwtPlhuLA MACULOSA 4 0.b 0.- 2 0.d4 Cw t P l uul, A PLA%4 37 7.4 0.- 31 16.SS P AmII.y CtN11NilDat C t .* l T at t a a d. esc Akun 24 4.s 0.= 19 W.ul FawILt caiLouse Lt.In AE A rs acHi s ont.3 4 ---). 0.6 0.- 5 l.J4 g FA4ELy > 15 5 0 w t. L t. l o a t'
; DIOUUh4 CAftht %15 1. 0.2 0.= 1 u.45
&Aalbf " a W6 t ht f.L l p a f.
~ -
p 4 A N G l .4 4.1.L a APICimA 36. 7.2 0.- II, 4.66 M tAMILf N A 5h a H I D A F. 1455awlHb eintA -- - --- - 3 0 6 - 6.0 1.* 19 1.5% --
- g. FAmlLV Wl5SDINIO4E MISSulmA SP. 1. 0.2 0.= 1 0.4S 7
Ln
,, PHILO* a w Tnw r ipuo s Class CwdSTactA S0.224 10.045 13.1012 2.1402 susCLAss C l w H I P Ltel a FAMILY HAL44lDAE " S. 1.0 0.= S. 2.24 natas.us SP. - -
sunchass m a t,aCo6Tw aC4 o g i>> > 130 pod 4 FAalLY SyNAENOW4Tidat n = I u . a* P . - - - 1 0.2 0.= 1. 0.4b OwotN A*PHIPavA F A m i t,Y 4*P1TH0luaF
- -16, 0.= u. 3.19 L_ s_,
u m f it. 6PP. 2.0 t' A m i t s aird lD A t o In. sPe. i. 0.2 0.- 1. 0.45 p,_ - todtbf at.L i f t p4E - - - - - - uselu. SP. 1. 0.2 0= 1. 0.45 ( OnLeM OfCAPODA
",. u-FanlLV A LP.st j p4 F ALPHeuS S k a l LL 4 filS 4 0.t 0.- 4. 1.79 a l.P st u s Hi Tt.wilC.4 a El l s 45, 9.0 1.= 18 6.h1 f._7 _
ALP tu6 h a .N = A = h ! --25 h.O O.. 16, 6 b6 e -- A L P h t.0 5 SP. 4 0.0 0.- 3 1.30 [
- F A ct I I, Y C 4 LI,1 & % a $ $ ] D A t' ,
HenW al A A t r t ail s 11 J.4 0.= 16, 7.06 b : ~-
^
6AwlLt HIPPHLi!luaf ,,.
- HiPesLyle Pt.t.na a C a m T H A 259 'J1.W l." 104 IO.40 v.
l'LuwlDA4uh A. 0.6 0.= 3. l.J4 - L- [ w O 6. _ 20 4.0 0.- 16 6.15 C-T u Z t.u = 4 C a w oL i se t h 5t taulty m a.! ! a A >. C L-i.t>I%Ia niew l a 2. u.4 0.- 2 0.u9 -, e a s t e.1 nG : s t i.a t Lp estw t ur s 3 A .4 0 l t s s l 5 t a M i s, y w a b.la t u A >. 7 l.4 c.- 4 l.95 {~ PAGuwus Spe. 15 1.0 1= 6 1.H1 eaalty p a tat ama luat e al.a t ans e to e j u a u a. 14 3m 0. IS 6.bu 9 9 9
~-
A>)l i, - l t p, ' i
-\ 1 l l ) l t f , ',
_ ' C/ { j h
' ' ( '; ] '
-(: 5; 2 -~ 3 8
e ce 3 I m @ F* E a% e N 4 es =3 4 2 e o e
>*=J 3 as
>4 Iw e Q e
- e e 4 1 OE ** O O 3a me Ow & .
O E f C 3 >.,3 m e e se 3 es =* 9 m E GH * - e 6* 0 Q @ O f= 5 B.= e e e 9 f* O N 5 0 8N 9 E @ @ d 9 s N to *
> 2 f* O e Ze o e e e
- O N v.e o S ia.
R
* =J e a @
A 4 @ M Pe g to 4 ** Po
>= 0 0 *
- e 2 8 > o N g
as
,,J
.e. se 1
1 > a e ==
- I ee r* e c =e ae J* o O P= 3>omm 9 se 5 1 6 a me e .3 4 3 9 9
- S e e r*
- ee =e 3 o e o e e e o e e O ea e e o e a e e e e
P=r= + 3 *
- e o
- 1 e eO mO3N NO O C 4 0 De
- 2 9 e A me 1 2 3 $ 4 2 mm 4l **
o e e o e o e e e
> cg ,, w e o e e e e e e e e* == 0
- e m == F* P* 6 == N O
- 1 @ = = = = e ** en ==
C ee
>= .3 = ee e==== .
m e at O. W X> == 2 m J OW D eQ 2 1 ma e= 02 9 m C32 OCe 0 0 t 5 0 g 6 8 0 0 8 0 t O O 4 9
- e *
- e e *
- e o e e * * * * *
- e aOV 2 o OOOOOO se o e 4 V me 4 .1 Oooo 3o O O L> > 1
>Z 24 ee as C O1 x1 a.s> e d OO Z 9
.J Z A3 m e & N Pe
=* ** L E eN &9 & Pe N Pe 3 39 9%9e e e e e e e e e o e e e e e a e e e a 4 4 1 e2 0 9 2 3 0 t e e O 3 == ee o O O m e e # Q == ** P=
2 6 m se 2 = =
- 0 1 E 9 &
V O? 8 4 >= 9
- e. U 9 3 0 o e e . . e o e o e x s e e e e e e e e
- se se me @ @ N m as r= Pm 3 en se to 6 e se 9 P=
m es se g*N f=t 9 g W $ 2 me
$8 ee i
2 T r T C 4 V : M > to e ==
== 5O W iC se C 2 2 3 : W d 4 4 V 4 em I QQ ea st 3 2 '", em os E W 2
'al == 2 12 W 4 he 3 ===4 6= 0a 7 e 4 e 4 14 ==o I 2 21 : C = 1a3 6 Z *=
* == 1e 3 e= == 4 4 E 0, e 2M 44 4 2 2 O n= ~4 = e: 2 4 4 iC # 4 m 4 W == 4 4 Z
- 1 1 4 4 C ae s s O e L *as D G: 9= L m k b= 1 m t* a= a y e. 1 >1J r t, 2 se e, I; 4 .
v 7 a a a a 4 /2 e 3 4 m *= *m T1 4 ,, 7
- 1 e et e ==
- 2 2 I E 4 12 V 4 V - De O != 1/4 1 2 % es 1 I 1
%# 4 V 14 > V
?--2 f) #2e Z ** Ow 2 X C 214 m 4 a 8 E 44=0 == *OJZ 44 4 2 2aC C >e I T 4 al L b e 1Y e I e 4 eU e e x . -- 14 e 1 ==O 1 2C 12O st - 1 =E T
>1 1 : za o=
v:
* = -
2 *= =_= - = * *
= 441 2 2 == F >= I N
21212.3 .a . 2 .O F*==7 O e= E 4 at i a > al 7 > - s= 4 n= to ; e I r CL#-F i ,11 : re: .:
=
u 1 1 1 1.a. l - - -
- v. : va :
1 1 1 1 Y A. E A s e 6 6 1 E A / 2 ; : wa T 2 9 .2 ./, e=e ; .
-- : -a .J 2, <2 -
= zu u
.- < ~ 1 1 1 - -
i i e ', ) ) ) ) )
- I-3-66
Table B-2. (Cont.)
=
. CONutLL mt T C Al t' L t001 MA5ft - C, Jle1 W e 'l, MPUNT FOR THIhD QUARTEk we'4TuwI >LowluA P0stw CokPOHATRON OVENALL g Coa 40487V STwuctuwt 57UDV AT rRYSTAL H!vEH Puot R PLANT
====----hu=Htu 36' IhulylpVAL6 --=-===
-------PtH SquApF mtTEk------ ----=tT mEIGHT==-- ===-DNV mEIGHT-----
, mEAN/M2 TAtug N WLAN MANGE STD Utv TuTAL m e. A N / M 2 To*AL TOTAL 1647. 32w.4 116.- 846, 299.14 330.660 66.132 192.3016 38.4615 g ,o O
9 s _ _ _ . . __ I tu S wJ O O 4 9
==;
o (C-(g L-
.s =: _a-w 9< .. _
C; W h-'- 7[ - w -- w k. C mM-CL
~
qD Tc 9 9 ee C5
Table B-2. (Cont.)
< C or. h t L t. me TC Al F 6 LDDV
.4 4 51 = - o t st.e 4 W r.t u t.PON T toH T H I 6f D Gu a u f h il y>N10wI tLONSDA Po e Lie CokPukATRON OVE. HALL Co 4 Mil d ! T V STHUCIUNL S1001 AT CWVSTAL k l V t' M P'). L N PLANr
- - = = = = = = N u m et t R OF thDIVIDUAL6--------
-------PtH SQU A Hl. htTEW------ ---- e t t h F l GH T = = = = ----DhY =[lGHT--**=
IAun N M t A B. HANGE STD tit V Tuf 4L PIAN /M2 TOTAL an E A P / se 2 PH V I.ls a *t:"f d f lN t A O.003 0.000 0.0004 0.0001 o*In. 5P. l. u.I 0.- 1. u 16e PHytow 4,ns Lina 2.591 0.369 0.4270 0.0610 Cl A w Pol V t.'u A t.1 A t' A M i l Y C A P I T El,1,1 h a t. H t:TewoMASTUS FILIFOWMIS 1. U.1 0.- 1. O.Je t A u lla V >HvlCluAt 4AhPHVSA SANGutht4 IS. 2.1 0.- S. 2.04
> A m t l. V 6LV Ct w Ils A t.
y i.L V Ct.H A A ktH IC Aas A FAMlbf Lu
- Mh 1 %e.H E l O A t'
- 13. 1.9 0.- 6 l.9%
g s LUwnkl*tWIS '
- l. 0.1 0.- 1. 0.J.
G tAmlLV M A I.4 4 = l H A v. W owANCHloA.%%CHIS A4tWICANA 1 0.1 0.- 1. 0.$u e A 411.V 'lLHEIDAL 4tWelb 6F. - 3 u.4 0.- 3. 1.13 041o. >P. 3. 0.4 0.- 1 e.S3 FAN [LV oW HlNI))) A L scoleopl.f ah HudWA b. u.7 0.= 4 1.50 PHVLH= =oLLusCA class nIVALvlA 2.423 0.346 1.9214 0.2145 tA*lLV CAWullOAt 1, A E V I C A w o l u u mowi0N1 1. 0.1 0.- 1 0.JH I _ tAmlLV 1.Vo4NIIDAE a.voss t A H V a is i r. A 1. 0.3 0.- 0.3W 'D) 1 urX tAmlLV %V ril.l L AE A vi.ou.u. e 4P v u t o.6 - 2. 0.3 0.- 1 u.49 hN a t A m tl.V SoltNIDAE ph
*:hs t s a l mow 1. u.1 0.- 1. 0.3d FaulLV v b w
- w t u a t' ~
C H l o a t. CANCtLLara 1. 0.1 0.- l. 0.sh :._ Tw Ardst st Lt. A CONw&DINA 1. U.1 0.- 1. n.Je , CLAbh 64hTwoPouA - 5.944 0.W49 4.6944 0.6'06 rA*lLV CtkIIHI!DAE - CL4fTHinn au sC A wile I. 0.1 0.- 1 0.3d F 4 a ll. V gasAAwinat URSSAhlHS Viet a 2S. ) . ti 0.- 13 4.S4 PNV1.HM AwiHwoPouA-Cl,4SN CWUSTACta 21.197 3.114 4.1821 0.5915 SH M Cl, A S S 4 AL ACIPst N AC A a*wht H 4 = P H I Pe e9 4 -- tAmlLi a iP8 8.INCIDAF oelu. SFr. 1. 0.1 0.- 1. O. le
& A m a l, V A4PlIHolaAk o%1n. .s P p . 2. 0.3 0.- 2 0.76 o h " >' u 1.t c 4 P. .n 4 6 & 4 l t, y 4 6 ,1* 64 . [ 11 A >
u . P.i > n ..e r e mc .in t l.13 11 1.1 c.= S. J.oh
i
,1.) \
\!.1,is\ ,i[i > ,
. . , '\ ,
li', i . M2 lr' ' i l' i '
.\a I '
jg )a Uj \g u O e eN e E E e%
- O W m3 e2 O ee 3 ** 4 "4 M a as Z les O O 4 2 OE
=4 e O O O* 4 Q E o
a >3 O #
== a4 I C ** *
- to eC P' " i ee *
- i I e +
e O O e e ce eE e% f*
- e= 2 ** N Ie N **
Ow wg O O fe, 3
>=
4J M s4 # e t= *e 4 e= aC A # 2 e s's *
- as e se O
=&
E D m e aw ee @ MSe 3 ABa aa Ne a 9 e@ == 3 m O == B e e3 @
- 9 @ 9@ A N* %* AA 9M A de A49 m ? N g g g e e o e e e o e o e e o e e e e o e e e 'm o e e e s e eS OO O .= 0 0 O =eo O O 3 3 NO O O O 3 == 0 O *e a e e ee ==
a, e e na un e2 m e Les 4 me to **
> 0g ,,3 w e e o e o e o e e o e o e e e e o e e e e e e o O at E N *e == 0 ** N ** ****e**==== # *e ** =* ***eN *e *
- C ==
* =.a. =
- W an e CW 3 ** ** 2 eJ 4 C 49 >4 53 21> =* O 7 wCzz oo4 ee a eee e eee ee e ae e e e ee e e e e 2 to 3 e a e * * * * *
- e * * *
- e *
- e * * * *
- 4m. e.WOW a= OO O @QO O OOOOOO OO O O OOOO O O O V ** em 2
>* Z 14 th W es Cd C .h 8 4 e se e MOO S e m3 2 13 me J De 1 e e se *
- 8't e == f= se se == e me W ** es e se M 3 9 as e se A 4 ud g e2 e e e e e e e o e e e e e e e e o e e e e e e e 2 3 3 e4 OO O 3OO O 33OO3O at O O 3 3 0 == O O ** **
2 == 4 e e* O 2 2 e E V 33 e J == e
*U e 3 e I a e o e .
- e e . . e = e e e e o e e *
- e e o e e .e. = e* .e
- e. **e N *N* , r= v .e n r= m . se a M
e e 2 e
.i.
{
. m l
.ie
'O m i
, i e
> , e i t
*= i l li 1
3 I I 3 C I A V l 3
@ es=
3 4 l , 4 ans O 4 40 I f I ' @ 7 3 3 1 e* '
'.ef 4 W W 2 4 E O == to I i 4 W, 2S == j 2 laJ P m 4 O E W == C +
e= m se .L i/* M 4
- W a= 0 e2 o J &4
- T = = = = 4 EA2 4 2=101 l' e ti 3 a.s 2 kJ E f 2 :. 2 3 ** Cm%AJA s14 K C4
- 4 A == ==
- 7 == 4 4 4c=4 4 e 4 E 4 & I'* J 4 ') %
- 7 *d Id A d Id 4 $ =4 id M 1 *E8 4 C 2 of m>1QE Ow 7mWW6 4 3 e m A A '4 4 C h / > > 'W C C14 4 =J ==*E =1 3 4e* W ** ee
., 26 m4 e 4 see 1 2 e- 4 2 4 A v
m T in =
- 4 1>O 242U2 s'l O e F 2 2 3 1 14 JJ a.4 e 3 e. 40 2 r 1 - *4 e as e
& 8= U U *= *= 0 1 1 1 > 1 3 e 21 w e Z1 C Ed IA J == k
- 4 4 O A J O O C == se id 2 W id 2 m O4 7 2 C 0 /24 4 e M 4 to 4 E : 4 : =* J
- f 4 34 1 T E JJ el = 022 24 4 7 7 2 3 e- T e 4 osQ4 ZO : Lz1awdUU esa e 1 == L C 4 64 4 e e
- e 4 U e g I I I C L2W = e4 4 --O 4 3 J m was: = 20 3=O V 1& O E O P4 O J =2 =J 2 x == 2 == 2 2 %O -e 2 == = = = = 3W l d aJ>1*-TO>4 >g 4 at 4 42 > w # m. 4 > t me O e 2 ? mp 2g T e. =Y=
CQ ** 8E *E J 2 J F 0* ** 3 1 J % & & 1 1 3 J 1 =1 is' E E 3O VO 2#T
== == == == me ==J V .2 . 4 e 2 g yO I T I E 1 *
- r 3 ed e == 4 4 4 4 4 4 4 4 &
M z * '.
- a e 4 w w : r ae g 2 2 2 @ ; ; en J
-> c J J4 f V 2 4 m m ,,3 Y 4 M 4 Z $U
%> h 1 1 4
I-B-69
0 Tal> 1 e B-2. (Cont.) L i s h h t i.L * > T C A l.) k k !> ts t
,-l THIfeD QUApTtB eeA514 - til scet a p66 h tPa WI DLk 6 Li>H ita A p p. 6. k Ce nW PuW 4 T ilig OvitaALL stN10wI CommuglTV STHuriuwt S T 't D i AT CHYSTAL HIVEN Pont e PL Aas t
...-----nuuhtu OF l as t a l W I DU A l.6--------
-------Pt= suupuE s t 16.H = -- - - * ==--WET mEIGHT---- ----DRV etIGHT----
T A gesh si McAM MAhCE Sfp 886 W Tui&L PLAN /M2 TOTAL MEAN/4J TOTAL 221s. 12.6 9.- 51 16.66 h l33 5.0l9 ll.0408 el.6985 H 03 i N O
,( n . _- -
f .
\
u
--~
~ -
l-f-
~
1. b A- > u
Table B-2. (Cont.) CommtLL mt TC Ar F 6 trnt NEPohT F eim Flus h T H ousett a eastu - Ca=TanL Odtk&LL frLttw ! O A Pe te t W Cfinrtik&fing VFmTUAI Coa *UW17Y STRUCTual STUOf AT CkT5faL SIvik P o e t. P PLAh7 i
==------gumeF# OF teetvtruAL3====----
---.---Ptu scua>L ktTLM---~~~ ====utf stICHT---- ----Cat = LIGHT-----
TOTAL plANin2 TOT &L praw/m2 n st an wahCF S T D r-t v taAne 90.940 1s.192 32.s197 6.5639 FHVLuw PowlFEka ~ 0.100 0.036 0.0852 0.0010 PHILum PLATTHtLM!hTHt$ 0.45 u-.D. SP. 1. 0.2 0.- 1 0.023 0.005 0.0042 0.0000 PHILUm mEntRTI4tA 2 0.11 untD. 5P, S. 1.0 0.- 0.261 0.052 0.048$ 0.0097 6 HILUM h!PUNCOLA 10 2.0 0.- 7 2.92 m unID. SP. _ . . . e 9.491 1.898 1.1047 0.3409 f FHTLUM SthtLIDA y CLAS5 POLVCHALTA - bd FAMILY AmFnawetlpar- - --
- 1. 0.2 0.- 1 0.4S mELim%4 maCULaTA FaulLY an a..t' LL I n st 14 S.e6 8.6 -0.=
a m a tst.L L a i k I cttLott - -- -----10.----- FantLY CAPITtLLIDAE 0.4% HEf t. Rom asTils FILIFOI* MIS 1. 0.2 0- 1.
------3. 0.2 0.- 6. 4.4b UNID. $P.
FantLY tuutCIDat 0- 46 19.72 mapPHISA 544CUIREA $6 it.2 FAntLy GLTCkulDAE - - - - - - - - - GLYCkHA AutWICANA 3. 0.6 0- 1. 0.5$ FA41LY maGtLONID&E e.46 .- e 66t.i n= A PETTIW=E st - -
- 1. 0.2 -0.- 3.
FAnlLy m & L u a m i n a t. 4RInTHtLL4 atCOSA 44 8.m 0.- le. 16.39 HMA>CHida6VCHl6 Amt k iC Am A -- 31. --- 6.d--- 0.-- 84 6.67 - -- F A M I t.f utkEIDAE LaFU4t.Nt!5 CULVERI 1. 0.2 0.- 1. 0.4%
=>WFIA Fal.64 -
1 0.2 e- 8. G.4%
>Ewtl5 suCCitt A S. l.6 0.- 6 2.61 et,4TVmfkFis numEMILII s. 1.6 0- 4. 2.49 -
u = I te . 6P. - - -- --- 3. e.6 0.- 2. 0.69 FA41L1 OEUPHIDAE DinPaTNA CitFhEA 1. 0.2 0.= 1 0.4S nh'iPH I % 4 t **u b415 4 --
- 42. 6.4 3.- 24 N.79 FAMIL3 OWH14(InaF H A PLHSCOLUPLO.% ROMUSTUS 1.s 0.- 4 1.4m 44tathEt6 6P. - - -
26 - 6.J 0.- 21. u.el .,- - SCDLOPLOS W U tq u A )). 6.6 1.- St. 610 t.,...-, F a u l t. T P6 CTIhau gin &F PF CT Im ap ia Ginitoll -
- 8. 4.2 0.- 3. 0.45 jd' family PH f L t.ohnc i n a E J.6 u.= II, 4.tw "9, 9 '.
t.f t UNt we'T F h nPuo A le. i~ tAmILt Poe C ILOC M at t t re A L pol C I L OC H a t.T u % J .)M ts in h l 1. 0.2 0.- 1. D.4% F&alty Paty%s) Inst 0.b4 6 t,6 P i p a n t i p l a Com m t g t. A L l t, 2 u.4 9 2. 9
9
~
Table B-2. (Cont.) COh=tLL m>TCALF & fnDY ktPowT snw FouwtP LU ANTl k NAstN - Com Twol. Ov f M ALL. Wrmfun! FLuetDA P uu t' N ComPumATlow Co==uMITT SThuCiuaE siuDT AT CRISTAL kIVtW Pont R PLANT
---------munstR OF INDivlDUAIS--------
-------FFa SouabE mtitH ----- = = =- e t T w i l G H T ---- ----DWV mLIGHT-----
WAhCL STU Ut v TOTAL ofAh/m2 TOTAL utAN/m2 N m t. A n gA10% LFPICOMuTuS SP. 1. 0.2 0.- 1. 0.45 FAmtLY 5 A nt t L10 A E 0.4% SantLLA utCm0PTMALMA -- 1. 0.2 0.- 1.
- 1. 0.2 0.= 1. 0.45 UNIO. SP.
Family SAptLLApllDAE ---
- 1. - 0. 2 - 0.- 1. 0.45 SABELLamIA v u LG A m ! S --- -- -
FAmlLY SEhPULIDAL 0.SS 0410 SP. 3 0.6 0.- l. FAMILY SPlug t f At -- - - PAWAPNinmOSPIO PINNATA 1. 0.2 0.- 1. 0.4S r4 FamILV SYLLinAF -2W. -11.40 -- - - - - - - - - - 3 SfLLIS SP. - - - - -
-- --- 4 0 e.0 --0.-
U3 Fam!LY TERLhtLLIDAE 7 3.05 LYSILLA ALMA g. l.6 0.= da PISTA CplSTATA- --
-----2.----'6,4 -
0.-- 9. 0.99 ra 0 u9 Siht hLnsoma H ART 4 AN AE 2. 0.4 0.- 2.
~
PetELum unLLUSCA 0.095 0.019 0.0427 0.0085 CLASS AmPalNtuMA FAMILY 15CHNOCHIT0mlDAF 0.- -6 2.83 - - ISCwmoCHITog P A P I LLOSU S - - - -- --- 8 0 - 2.0 2.003 6.0973 1.2195 10.416 _ _ _ ,- 1 ;_> class nIv&Lv!A 9 0.- 3. 1.30 _l LatvtCanDium u0a7041 1.s -- i _- t FAmity CAholTluat- - - - - --- - -- 4 0.8 0.- 3 3.30 CARDIT4=ENA ELORIDANA FaulLv LYuwSIIDAE e.- 2 0.64 i Lynhila HVal,1NA 4. 0.# FAMILY mfTIL!bAE I SC M ali t u m utrunvum 3. 0.h c.= 2 0.s9
--- 7 -
1.4 9.- - 4 l.9S - _ _ _ . . muSCULu3 L A T E M A b l o -- - - - --- - FA4!LY OSTkEinAE 6 2.51 CHA55nsTwtA vipG!WICA 8 1.6 0.- ,_ OSTWLA Eu"FSt#15 1. 0.2 0.- 1 G.4S t 44 II.V T6LLlhlDAE 7t.LLINA SP. 2. 0.4 0.- 2. 0.e9 fAalbf WehtWIDAE -- - - - - - - - - - - - 7 l.4 0- 6 2.61 TRAmsthtLLA CU%AADINA 92.167 10.433 75.8586 15.5751 CLAS5 CASINOPoUA FAMILY MuttlpAL - - - - - -- kul La NTHIATA 2 u.4 0.- 2. G.sw FA4!LY CHEPIOULIDAE 107 44.94 - - - Z-T CH+PIDuLA m ACul,064 - - - lbS.- 31.0 0.- 29 S.t 0.- 29 12.42 CwtPIDulA PLAhn F Amil y CANCElLA9inAt CanctLLadla W6TICubaTA --
- 2. O.4 0.- 1. c.%%
Fam!Ly CtMITMl!DAF CtplTHIHu musCAwud 44 h.h 0.- II. 12.m3 S. l.4 6.- b. 2.24 CtWitHlu" 6P. FAulLy ColumetLLinAE A N ace 41 A StelPLICATA 1. 0.2 0.- 1. 0.4$
Table B-2. (Cont.) Comme ( L stTCalF 6 600T masIn - C64th11 e t Fout 6 ou enesTH c.u a h T t h vtmTURI PLUptpa Poet > CLmpupATIOm OvtP&LL CD= mum!TV SThbCTuut 5f Los AT CPtsTaL hIwtu Poets FLah?
- -- --= =----m u m p r e nr l u e t v i ms t L S --------
-......Pgp scuapE wtT6R=----- ----nff HEIGHT ==== ----D8Y mEIGHT-----
h mLAh kamLL STD L6y INTAL mean/p2 TOTAL pt.Anim2 TAA0m Fam!LY LPITunt! Cat FPITomIUm SP. 4. 0.2 0.- 1 0.4S Fam!LY maWGimELLTear - - - - - - - - maNGIhtLLA APICl44 10h. 28.2 1.* el. 22.52 FapIt y mELo=GENIDAE trLomCtea conomA- - - - -
-1. -0.2 0.- 1 w.45 Fam!L1 muu! CIDAL CALAfanPaum 05faEARUm 1. 0.2 0.- 3. 0.45 eantLy e a s s & t t n a e --- - -- ----- --- --- - -
nassau!US v!HER 1 1.4 0.- 2. o.o9 FAMILY NaTACinaE l' c3 Pot,I w t C E S DuPLICafus-FAmlLY OLIvtLLIDAE
- 1. -- - - e . 2 - 0.. t. 0.4S 1 OLIvELLA SP. l. 0.2 0.- 1. 0.45 N . _ _ _ _ _ _ _ . _ _ . _ _ _ _ . __.
PHILua AdTHwovoCA Class CausTACr4 25.667 S.137 6.6065 1.3217
$U8 CLASS M A L A COST h a C A --- - - - - - - - - - - - - - - - - '
OncER 330p004 family CIROLAmIDAE Uhl6 SP. -
---4.-- - Get 0.- 4 l.14 Fam1Lv SPHaEpamaTID4E UNIO. $P. 3. u.J 0.- 1 0.45 ORDFR AmPHIFoda - - - - - - - - - - -
FAMILY A4PtLI5CIDAE Uh!D. SPP. 3. 0.6 0.- 2. 0.09 FaulLT ampITHOIDae- - - - - - - - UmID. SPP. 11, 2.2 0.- S. 2.Je ,- FAMILY anktDaE L-3C3, 0=10 SPP. - - - - - - -
-3 ti . 6 - - - 6.-- -3. s.34 !b FAm!LY mELITIDAE (C,-c UNID. SP. 2. 0.4 0.- 1. 0.55 ~7 DaDtp OEcaPona - - - - - - - - - - - --
,-7.,.
FAm!LY aLPutIDaE g-; gj, at.Pse us Ht Tt ROCH AELIS 1. 0.2 0.- 1. 0.4% 5 9 ALPwtels mi)mmath! - - - - le ~ Wee Ge* 2. DebW aLPMF us SP. 1. 0.2 0.- 1. 0.45 f .;07 Usin. SP. 1. 0.2 0.- 1. 0.45 ( -? FaulLt C a t.L l a m ah51 Da L - -- c T et UPoctngA Aprim35 18 3.6 0.- 12. 4.9v ^ FAmILV HIPPULVTIDaE cC [7 MIPPOLITL P LE **w a C A g f M A - - - - 03 29.6 G.* #9 Ja.63 (cf u:: FAMILY e4JtDat - UNID. 5P. Pa60wtoaE 1 0.J 0.- 8. 0.45 If}lf,' Famit.y FAGuhus SPP. th. 3.2 3.- 7 2.om ",i f Family pata;aq=Inaf Cy, P a L A > H+4 FLoHlbawdb 3e G.6 0.- 3. 1.34 b'- Y ' P AL At mo%t Tt 5 1%TtH4tDIUS 3 0.6 C= 3 3.34 g PthlCLInt%ts AuthlCahus 18, 2.2 0.- 7 3.tv O O O
0 Table B-2. (Cont.) CohhtLL mtTCALF 6 tDDV FouwTn QUApttu FtPOHT FOR OWIRALL HA$lN = CnNTHOL FLowlDA Pnuty ConPopATION VEhTUat ConMUNITT STWbCTUNL STUDV AT Ch15TAL plVLH FOutM PLANT
= =====--mu*MtR OF f h D ] W J DU A 1, $ = ===== = = ----095 *EIGHT-----
===-===FLN suuAht utTtR--==-- ====hET WEIGHT *-==
TOTAL ptAN/m2 TOTAL "f4*/m2 N *LAh WA=Gt STD Otv Yan0N
- 12. 6.4 0.= 16 m.32 PFW3Cl.latNL5 LONGICAUDATuS 0.= 1. 0.45 UNID. SP. 8. 0.2 FAMILY PMOCVS1]DAR 1.#2 AmeIDLETtW SY4=tTRICHS u. 1.6 0.= 4.
F A m t l, V EANTH[pAE
- 3. 0.6 0.= 3 l.34 EURYPANOPFHS DEPR ESitiS 36 6. 'i l 20, 4.0 0.=
EUNIPANOPFHS SP. 1.10 NEOPA40PE PACKARDI 4 O.# 0.= 2. 1 1.4 0.= 6 2.61 NFOPA40PE TFXANA IS. 6.Sh
- 28. S.6 0.-
NtoPAm0PE SP. 0.- 4 1.19 H 4. 0.8 ~- WITHhHPANOPLUS -- - HARHI5tl- - - - - - - - ~ ~ ~
- 12. 2.4 0.= 17 S.)?-
UNID. SP. I 7.408 1.480 3.0120 0.6844 'J PHILUm LCHINODENmATA 3.9 0.= -19 -7.9% U UNID. SP.
- - - St.
PHYLUM CHiiRD AT A -- - - -- - - - --- - - - - 13.845 2.629 3.2231 0.6446 CLASS ASCIDIACFA- - - - 0.= St. 12.S8 45 9.0 0.2746 UNID. SP. 5.979 l.196 1.3581 CLASS OSTF.lCHTHYES 1.4 0.-- -9 3.45 - -- UNID. SP.
-- -- 17 C~:,
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UH b= 1 r* i 34 bd l j
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1 e 3O & 9 , l JA&3 h 9 f j J > E 9 M 4 t 4 4 W3 E f 3 e ; j A Q D 0 e e l I I 1 j g 2 ad E se M !
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C U v d OJ i u Q s 0 a5 m c 4 MF st
- 4 s e CD k
( 4 6 S S 3 3 8 3 3 3 8 ) I i ' ( ( 6 4 4 4 I-B-75
y -
= 3
= 2 'L ' 5 '
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h = / 6 5 3 4 3 3 -
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>A Ta HL
! 0 0
0 0 0 0 0 4 3 1 -('~c f' t (s. a 6 a> Gm C. I 0 0 0 9 9 0 ut av E O = H T yL pA 1 6 3 9 0 9 R 2 5 1 - L r T 1 8 9 3 0 4 8 8 C = O 4 0 0 0 0 8 9 I = T -
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3 0 0 5 TN 6 0 4 0 H& 0 0 0 - Gt 0 0 0 I h 0 0 0 - L - D f - t L mA
= T 2
9 7 0 3 5 f l 5 5 3 5 9 0 y-
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h = T U. e. A = 0 0 0 0 0 6 L P - N v 2 3 9 9 u8 s )96S . 62 b #7 1 a 8 9 3 9 v3 9 37 l 1 5 L = = i 5 4 4 l 3 j n = = L 3 5 7 1 7 384 5
. 8 7. %. I 3 . . $.
u = = 0 l 0 1 0 0l0 e 0 O 0 O00 1 00O4 3 1 00l 1 P = = U l 2
= = T u =
- S l = M v = L v
nl i ST Lt . . . . . . . . . . . . . . . . . . . . .95 . .114 . . 4. i t b I A M 1 4 2 1 2 lS1 0 2 1 1 1 1 1 - S2%l 5 1 1 t H S o TL A A t eT Dt t k t 6 nS e4 G F. op N t h nC wrV l Hm nUA hS W
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1 0. ). - 10WUl l1 00e 0 O 0 - 0 0 0 - G1 u 8 1 0 0 00d - 4 D 0 = A - h l E u=t - O p E = s - - - - C uU = - - LT = - - - FC = - U H
=
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- u M M 4 M m 4 A A 4 A A A a A A B = !
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f = O - h = T - - 6 4 - 6
& = 2 L 0 P -
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.=.
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- a C Ou - - -
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= . . . . . . . . . .. .
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m - u m m - o - C - - e - - - t - - - l H - - - -
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Table B-2. (Cont.) CommLLL utTCALF 6 EDDY eA514 = DISCHARGE HEPOpi Fna POUATM QUAhffa WLuTURI ~------ 'FLONIDA Posta Coprnwaffem ovERALL C0auU4ITV SfauCTukE STuot AT ***%TAL RIWLR P0mE8 PLA47
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I-B-81
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., 6 Cl!CHASCE 2.58 C.69 2.99 0.88 i 7 Cl!CHAEGE 2.e5 0.74 2.46 0.91 c:: Cnts ALL CISCeaeGE 3.63 0.88 2.19 C.57 [o ,3 3.36 0.74 9 w e 6. e W w
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