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
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.
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.
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 |
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%,
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.
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 |
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 |
|
|
|
|
|
Boat Activity Survey |
Stratum: SW Coast |
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 |
|
|
|
|
|
BAC = (5 + 4 + 6 + 5 + 1 + 7)/(8 + 9 + 9 + 12 + 3 + 15) = 28/56 = 0.5The characteristics of the approach are as follows:
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:
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:
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.
9.9.1 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:
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