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9. BOAT ACTIVITY SURVEYS


9.1 OBJECTIVES OF BOAT ACTIVITY SURVEYS
9.2 TARGET DATA POPULATION AND ACTIVITY STATUS
9.3 SAMPLING REQUIREMENTS
9.4 BACS RELYING ON FRAME SURVEYS
9.5 SAMPLING FOR BOAT ACTIVITIES
9.6 COMBINATION WITH LANDING SURVEYS
9.7 BRIEFING OF DATA COLLECTORS
9.8 IMPLEMENTATION ASPECTS
9.9 FREQUENT PROBLEMS

9.1 OBJECTIVES OF BOAT ACTIVITY SURVEYS

The primary objective of a Boat Activity Survey is the formulation of Boat Activity Coefficients (BAC), which represent the probability that a fishing unit of a given boat/gear type will be active on any day during a month. BACs are then combined with raising factors resulting from Frame Surveys and Active Days Surveys for estimating total fishing effort within a minor stratum, month and boat/gear category.

Boat Activity Surveys also assist in assessing the general accuracy of previous Frame Surveys through sampling (see section 8.10), as well as for recognizing significant changes in the fisheries.

9.2 TARGET DATA POPULATION AND ACTIVITY STATUS

The target data population of a Boat Activity Survey is the activity status of all operating boats on all days of a reference month. The activity status is set to one if a boat has been found fishing on a given day, or to zero if it has not.

Example: In a minor stratum during April (30 days) there are 100 gillnets. The target data population consists of 30 × 100 = 3,000 status elements for the month that are either 1 or 0. If the number of “active” (= 1) status indicators is 1,500, the BAC will be computed as 1,500/3,000 = 0.5.

9.3 SAMPLING REQUIREMENTS

The target data population is thus the number of fishing boats (as estimated by a Frame Survey) multiplied by the days in the month. Since the Boat Activity Survey is a sampling approach, the question is, How many of the target data population should be sampled to ensure that the estimate is representative of the entire data population? Or: What is the safe sample size for estimation of the BAC? (see also section 4. General Sampling Considerations).

Table 9.3 BAC sampling requirements at varying accuracy levels and data population size

Accuracy (%)

90

91

92

93

94

95

96

97

98

99

Data Population size

Safe sample size for BACs

300

73

85

100

119

141

168

200

234

267

291

400

77

91

109

132

160

196

240

291

343

384

500

81

96

115

141

174

217

273

340

414

475

600

83

99

120

148

185

234

300

384

480

565

700

84

101

124

153

193

248

323

423

542

652

800

86

103

126

157

200

260

343

457

600

738

900

87

105

129

161

206

269

360

488

655

823

1000

88

106

130

164

211

278

375

516

706

906

2000

92

112

140

179

235

322

462

696

1091

1655

*see notes 3000

93

114

143

184

245

341

500

787

1334

2286

4000

94

115

145

187

250

350

522

842

1500

2824

5000

94

116

146

189

253

357

536

879

1622

3288

6000

95

116

146

190

255

361

546

906

1715

3693

7000

95

117

147

191

257

364

553

926

1788

4049

8000

95

117

147

191

258

367

558

942

1847

4364

9000

95

117

148

192

259

368

563

954

1895

4646

10000

95

117

148

192

260

370

566

964

1936

4899

15000

95

118

149

193

262

375

577

996

2070

5855

20000

96

118

149

194

263

377

583

1013

2144

6488

25000

96

118

149

194

264

378

586

1023

2191

6939

30000

96

118

149

195

264

379

588

1030

2223

7275

35000

96

118

149

195

265

380

590

1036

2247

7536

40000

96

118

150

195

265

381

591

1039

2265

7745

45000

96

118

150

195

265

381

592

1042

2279

7915

50000

96

118

150

195

265

381

593

1045

2291

8057

> 50000

96

119

150

196

267

384

600

1067

2401

9602


The above table indicates recommended sample sizes for estimating BAC at a desired level of accuracy. In a sample-based survey for basic fishery data, the minimum accuracy level of an estimate is empirically set to 90%.

Safe sample sizes are a function of the population size but for populations with more than 50,000 elements (equivalent in one month to about 1800 boats in the stratum) their differences are practically negligible. For a graphic interpretation of the table see also Figure 4.3.

Notes on the table:

Sample sizes are interpreted as follows:

In the example given in 9.2 the data population BAC was 0.5. The data population size is 3,000 (100 boats x 30 days) and related safe sample sizes at varying degrees of accuracy are indicated in the highlighted line.

At a desired accuracy level of 95%,

At a lower level of accuracy, to 90%,

9.4 BACS RELYING ON FRAME SURVEYS

This is a commonly used approach for formulating BACs and has been addressed in detail in section 8.3. On each sampling day data collectors visit a number of pre-selected homeports and record the total number of boats that were found active at these sites. This total number is then divided by the total number of boats indicated by the Frame Survey. An example data collection form for this approach is given by Table 9.4.

9.5 SAMPLING FOR BOAT ACTIVITIES

In this approach no use is made of frame survey information. BACs are calculated on the basis of representative samples of boats that are interviewed to determine their state of activity on a sampling day. Frame survey data are only used as raising factors. An example data collection form for this approach is given by Table 9.5.

Table 9.4 Boat Activity Survey - data form with Frame Survey data

Boat Activity Survey

Stratum: SW Coast
Homeport: Channel

Recorder: Samuelson

Active boats


Trawlers

Gillnets

Beach seines

Castnets

Traps

Frame data

10

30

9

12

11

Day






1






2






3






4

5

12

3

1

4

5






6






7






8

4

14

2

5

2

9






10






11






12






13






14

6

20

3

4

7

15






16






17






18






19






20

5

9

3

5

6

21






22






23






24






25

1

5

0

2

3

26






27






28






29

7

18

4

6

8

30







Table 9.5 Boat Activity Survey-form showing sample numbers

Boat Activity Survey

Stratum: SW Coast
Homeport: Channel

Recorder: Samuelson

Active boats

Day

Trawlers

Gillnets

Beach seines

Castnets

Traps

1






2






3






4

5/8

12/19

3/6

1/4

4/8

5






6






7






8

4/9

14/22

2/5

5/8

2/6

9






10






11






12






13






14

6/9

20/24

3/5

4/9

7/11

15






16






17






18






19






20

5/12

9/16

3/8

5/6

6/13

21






22






23






24






25

1/3

5/12

0/5

2/5

3/8

26






27






28






29

7/15

18/19

4/9

6/12

8/10

30







In the example 9.5 data recorders indicate the number of boats found active out of the number of boats sampled. For instance, 5/8 for trawlers means that 8 fishers were asked and 5 answered that they were fishing, while three specified that they were not. Therefore, the BAC for trawlers is:

BAC = (5 + 4 + 6 + 5 + 1 + 7)/(8 + 9 + 9 + 12 + 3 + 15) = 28/56 = 0.5
The characteristics of the approach are as follows:

9.6 COMBINATION WITH LANDING SURVEYS

At times it is convenient to combine Boat Activity Surveys with Landings Surveys. This can be done using a single form as follows:

In the example given above the form used for the recording of landings is also used to capture boat activity data.

Landings of a boat were sampled on 17 March 2001. In addition to landings information for effort parameters and species composition, the fisher was asked to specify if he went fishing on the three previous days. This was indicated by a 0 or 1 in the boxes printed on the right part of the form. The following three assumptions have been made:

The characteristics of the approach are as follows:

9.7 BRIEFING OF DATA COLLECTORS

Providing data collectors with precise and unambiguous instructions is fundamental for the reliability of the data obtained through Boat Activity surveys.

The following points are important in briefing data collectors:

9.8 IMPLEMENTATION ASPECTS

Implementation of successful Boat Activity Surveys needs careful planning including:

Pilot phase: small scale testing (e.g. within one or two landing sites) to identify possible design and operational drawbacks and to assess likely timeframes for full-scale operations.

Testing of the entire sampling programme: combine a pilot implementation of the Boat Activity Survey with the entire sampling programme for catch/effort assessment (normally 6-12 months) to ensure both meet their requirements.

Evaluation and revision phase: forms and classifications are revised and new instructions issued to data collectors.

9.9 FREQUENT PROBLEMS

9.9.1 Timing of field activities

9.9.2 Multiple use of fishing gear

BACs must be formulated according to survey standards and for each boat/gear element of the related classification. A frequent problem is that of boats operating different gears, which might be sequential or concurrent. Sections 8.3 and 8.4 provide some guidelines on these aspects.

9.9.3 Migration of fishing units

The migration of fishing units distorts the presence/absence of boats at homeports and for this reason the sampling approach should be used for formulating BACs.

9.9.4 Outdated frame surveys

Sampling at homeports for BACs should take place on an equal number of days, so as to rely on the relative accuracy rather than the absolute accuracy of Frame Surveys.

If no significant migration of boats has occurred and sampled homeports show a consistent increase or decrease of boats not accounted by Frame Survey information, this might indicate that overall increases or decreases have occurred to the fishery and a new Frame Survey should be implemented, or its present contents adjusted to reflect such changes.

SUMMARY

This section on Boat Activity Surveys completed the discussion on methodological and operational aspects of surveys that are involved in the estimation of total fishing effort using the Boat Activity Coefficient, including:

  • Objectives of Boat Activity Surveys.
  • Target population.
  • Sampling requirements and safe sample sizes achieving a desired level of accuracy in the estimation of BACs.
  • Commonly used sampling approaches.
  • Need for training and effective briefing of data recorders.
  • Pilot implementation, feedback and survey expansion.
  • Frequent problems in Boat Activity surveys.


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