10.1 OBJECTIVES OF LANDING SURVEYS
10.2 SAMPLING REQUIREMENTS
10.3 A GENERAL-PURPOSE FORM
10.4 CASE STUDIES
10.5 TRAINING OF DATA COLLECTORS
10.6 BRIEFING OF DATA COLLECTORS
10.7 IMPLEMENTATION ASPECTS
10.8 FREQUENT PROBLEMS
In this section the methodological and operational aspects of sample-based Landing Surveys are presented, including:
Landings Surveys are conducted at landing sites with the purpose of collecting sample data on total catch and species composition, associated effort, and other secondary data such as prices and fish size (in weight units). In this handbook the following basic data are described:
The primary objective is to formulate, on a sample basis, overall CPUEs and species proportions within the estimating context of a minor stratum, a calendar month and a specific boat/gear category. Section 2.1 has provided guidelines in relation to this process.
In Landing Surveys sampling requirements and safe sample sizes to achieve minimum accuracy levels are different from those used in Boat Activity Surveys. This stems from the fact that the target populations of landings are much less demanding in sample size than those of boat activities.
Safe sample sizes in Landing Surveys are determined on the basis of:
The population size for landings is usually set at the theoretical maximum number of landings that can occur during a month. For instance, if 100 trawlers in a minor stratum operate in June 2001, then the maximum possible number of landings is 30 × 100 = 3,000 landings. Based on that limit and the desired level of accuracy it is possible to determine the number of samples that will be required at the end of a month.
Table 10.2 indicates recommended sample sizes for landings at a desired level of accuracy and as a function of data population size.
Table 10.2 Landings Surveys 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 |
29 |
35 |
43 |
54 |
69 |
90 |
120 |
163 |
218 |
274 |
400 |
30 |
36 |
44 |
56 |
73 |
97 |
133 |
188 |
267 |
356 |
500 |
30 |
37 |
45 |
58 |
75 |
102 |
143 |
208 |
308 |
432 |
600 |
30 |
37 |
46 |
59 |
77 |
106 |
150 |
223 |
343 |
505 |
700 |
31 |
37 |
47 |
60 |
79 |
108 |
156 |
236 |
373 |
574 |
800 |
31 |
38 |
47 |
60 |
80 |
110 |
160 |
246 |
400 |
640 |
900 |
31 |
38 |
47 |
61 |
81 |
112 |
164 |
255 |
424 |
703 |
1000 |
31 |
38 |
48 |
61 |
82 |
114 |
167 |
262 |
445 |
762 |
2000 |
32 |
39 |
49 |
63 |
85 |
120 |
182 |
302 |
572 |
1231 |
* see notes 3000 |
32 |
39 |
49 |
64 |
86 |
123 |
188 |
318 |
632 |
1549 |
4000 |
32 |
39 |
49 |
64 |
87 |
124 |
191 |
327 |
667 |
1778 |
5000 |
32 |
39 |
50 |
64 |
87 |
125 |
192 |
332 |
690 |
1952 |
6000 |
32 |
39 |
50 |
65 |
88 |
125 |
194 |
336 |
706 |
2088 |
7000 |
32 |
39 |
50 |
65 |
88 |
126 |
195 |
339 |
718 |
2197 |
8000 |
32 |
39 |
50 |
65 |
88 |
126 |
195 |
341 |
728 |
2286 |
9000 |
32 |
39 |
50 |
65 |
88 |
126 |
196 |
342 |
735 |
2361 |
10000 |
32 |
39 |
50 |
65 |
88 |
126 |
196 |
343 |
741 |
2425 |
15000 |
32 |
39 |
50 |
65 |
88 |
127 |
197 |
347 |
760 |
2638 |
20000 |
32 |
39 |
50 |
65 |
89 |
127 |
198 |
349 |
770 |
2760 |
25000 |
32 |
39 |
50 |
65 |
89 |
127 |
198 |
351 |
776 |
2838 |
30000 |
32 |
39 |
50 |
65 |
89 |
128 |
199 |
352 |
780 |
2893 |
35000 |
32 |
39 |
50 |
65 |
89 |
128 |
199 |
352 |
782 |
2933 |
40000 |
32 |
39 |
50 |
65 |
89 |
128 |
199 |
353 |
785 |
2964 |
45000 |
32 |
39 |
50 |
65 |
89 |
128 |
199 |
353 |
786 |
2989 |
50000 |
32 |
39 |
50 |
65 |
89 |
128 |
199 |
353 |
788 |
3009 |
> 50000 |
32 |
40 |
50 |
65 |
89 |
128 |
200 |
356 |
800 |
3201 |
Sample sizes are interpreted as follows:
At a desired accuracy level of 95%, for a data population of 3000 (= 100 boats × 30 days) with an overall CPUE of 5 kg/day:
- 123 landings should have been sampled by the end of the month.
- The safe sample size of 123 corresponding to an accuracy level of 95% will assure that, at worst, the resulting CPUE estimates would be as high as 5.5 or as low as 4.5 kg/day.
- Assuming that sampling occurs during 10 days then about 13 landings should be sampled on each sampling day from the sampling sites in the minor stratum.
At a lower accuracy level of 90%, for the same data population of 3000 with an overall CPUE of 5 kg/day:
- the corresponding safe sample size is 32.
- At worst the overall CPUE would be then be estimated at between 4 and 6 kg/day.
- Assuming that sampling occurs during 10 days then about 4 landings should be sampled on each sampling day from the sampling sites in the minor stratum.
There are five key areas that should form part of a Landings Survey form, although their detailed design depends on their data coverage and intended use. In the example below optional data are shaded.
Part A - Document Identification
Landings Survey forms should always be identified to facilitate the organization and filing of hardcopy information, and cross-referencing between hardcopy forms and computer records.
Usually documents are identified by sequential numbers assigned as either:
Part B - Sampling Activity
Part C - Fishing operation
Part D - Species information
Part E - Supplementary information and remarks
Information on fishers, fishing units, events occurring at sites, etc.
The data on this form show that:
Trip Duration was 3 days. All catch was sampled (45 kg). Total values of other species was recorded as well as prices/kg by species. Associated sample effort is (1 unit) × (3 days), or 3 boat-days.
The following paragraphs present a number of frequently encountered landing types and discuss the use of catch and effort parameters.
10.4.1 Sub-sampling for large landings
C. Fishing Operation |
|
Boat/gear: |
Handline |
Number of Units: |
1 |
Duration: |
3 |
Total landing: |
450 kg |
10.4.2 Boats landing together
C. Fishing Operation |
|
Boat/gear: |
Gillnets |
Number of Units: |
2 |
Duration: |
3 |
Total landing: |
120 kg |
10.4.3 Fishing units with multiple operations per day
C. Fishing Operation |
|
Boat/gear: |
Beach seine |
Number of Units: |
1 |
Duration: |
0.5 |
Total landing: |
100 kg |
Such cases can be a problem. They generally apply to fishing units that can operate several times during a day, such as beach seines. The following points should be explained to the data recorder:
1) If the recording is done at the end of the day, the fisherman would specify how many times he operated during the day. This number will be used to calculate trip duration as a fraction of a fishing day.10.4.4 Processed or packed fish2) If the recording is done earlier in the day, the fisherman would be asked to specify if more operations would follow and the total number then used to calculate trip duration as a fraction of a fishing day.
3) If there were doubt as to the reliability of the number of operations, it would be preferable to drop the sample from the dataset of sample landings.
If processed or packed fish landings occur occasionally then they should simply be ignored in data collection. However, if they are regular then conversion factors that enable calculation of whole fish weight from processed fish weight need to be developed and used in the estimation of total landings.
10.4.5 Catch sorted by commercial size category
If all landings have been sampled then they should all be combined into a single form as follows:
INPUTS |
||
|
Total landing: |
100 kg. Effort: 1 boat-day. |
Total large species: |
60 kg. |
|
Large species A: |
40 kg. |
|
Large species B: |
20 kg. |
|
Total small species: |
40 kg. |
|
Small species A: |
30 kg. |
|
Small species B: |
10 kg. |
|
RESULTS (on a single form) |
||
|
Total landing: |
100 kg. Effort: 1 boat-day. |
Species A: |
70 kg. |
|
Species B: |
30 kg. |
1. Using a single form |
||
INPUTS |
||
|
Total landing: |
1000 kg. Effort: 1 boat-day. |
Total large species: |
600 kg. |
|
Sampled large species: |
20 kg. |
|
Large species A: |
15 kg. |
|
Large species B: |
5 kg. |
|
Total small species: |
400 kg. |
|
Sampled small species: |
10 kg. |
|
Small species A: |
6 kg. |
|
Small species B: |
4 kg. |
|
RESULTS (on a single form) |
||
|
Total landing: |
1000 kg. Effort: 1 boat-day. |
Species A: |
15/20 × 600 + 6/10 × 400 = 450 + 240 = 690 kg. |
|
Species B: |
5/20 × 600 + 4/10 × 400 = 150 + 160 = 310 kg. |
2. Using multiple forms |
||
Form 1 |
||
|
Total landing: |
600 kg. Effort: 0.5 boat-days. |
Sampled: |
20 kg. |
|
Large species A: |
15 kg. |
|
Large species B: |
5 kg. |
|
Form 2 |
||
|
Total landing: |
400 kg. Effort: 0.5 boat-days. |
Sampled: |
10 kg. |
|
Small species A: |
6 kg. |
|
Small species B: |
4 kg. |
10.4.6 Non-fishing boats landing catch
Generally, such landings need not be sampled because they do not provide information on the sample effort associated with the catch.
10.4.7 Migration of fishing units
In theory, the migration of fishing units only affects effort-related surveys. There should be no reason for not sampling landings from boats that operate from sites different from the one being visited. In fact, this is the correct approach at locations that are only landing sites and not homeports. Usually it would be preferable to give priority to local boats and include non-local boats only when the total number of samples is below safety limits.
Compared to effort-related data collection schemes, Landings Surveys are less demanding in sample size but require more skills on the part of data recorders. Lack of adequate training has direct implications on the reliability of data relating to total landings, catch by species, prices, values, sample effort and fish size. The following major points should be considered in this respect:
Fishing operations
- Identification of boat/gear type
- Cases when samples should or should not be taken
- How to obtain representative samples from boats that are landing
- Effective ways of measuring or eye-estimating total catch
- How to correctly record sample effort data
Species composition
- Species identification
- Effective ways of measuring, or estimating by eye, catch and number of fish by species
- When and how to obtain information on first-sale prices or values
Providing data collectors with precise and unambiguous instructions is fundamental for the reliability of the data obtained through Landing Surveys, including:
Implementation of successful Landings 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 Landings 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.
Supervision and assistance: Supervision of data collectors is essential for ensuring that data collection is conducted according to planned procedures and schedules. Typical supervisory functions involve:
- Ensuring that recorders visit landing sites according to work schedules and perform their job as instructed
- Checking the way data are sampled and recorded
- Ensuring that recorders are equipped and make effective use of items essential for their job
- Back-reporting of problems relating to movement, timing of visits and duration of stay at sites
Data editing and checking: Data collection forms are usually reviewed prior to processing, including:
- Organizing field documents to facilitate subsequent processing by grouping forms by Month, Minor stratum, Landing site, Boat/gear type, Date, or in any other sequence that will be convenient to the data operators
- Checking that sites and boat/gear types are recorded according to survey standards
- If species are not printed as a standard list, checking the species names recorded by the data collector
- Calculating species catch totals for cross-checking purposes
- Spotting suspiciously high or low values in catch, prices and sample effort data
- Controlling the number of samples for each estimation context (minor stratum, month, boat/gear type)
Timing of field activities
Selection of landing sites
Concurrent use of fishing gear
SUMMARY This section presented Landings Surveys, thus completing the discussion on methodological and operational aspects of surveys that are involved in the estimation of total catch, including
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