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3.4 Counting methods
 
 Methods may be modified depending on combination of the criteria used for judgement of viability. Following are two examples of the methods.
 
3.4.1 Counting method using morphological change and mobility as criteria for judgement of viability:
 
3.4.1.1 For organisms of the L size group, samples prepared by the procedure described in the paragraph 2.1 and 2.4 must be observed under a compound or a stereo microscope. Among organisms in the samples, only viable ones judged by their appearance and color shall be counted. If judgment of the viability is difficult, use a biological microscope at a higher magnification. if there are organisms to be included in the S size group, keep a record for calculation of the number of S size organisms in the sample.
 
3.4.1.2 While the volume of the sample subjected to a one-time microscopy observation shall be arbitrary, microscopy must be continued multiple times, and the total volume of concentrated samples for microscopy shall be equivalent to or more than 1m terms of the original volume of the sample before concentration.
 
3.4.1.3 For organisms of the S size group, samples prepared by the procedure described in the paragraph 2.2 and 2.4 must be observed under a compound microscope. Among organisms in the samples, only viable ones judged by their appearance and colour shall be counted. Though the volume of the sample subjected to one-time microscopy is arbitrary, microscopy must be continued multiple times, and the total volume of concentrated samples for microscopy shall be equivalent to or more than 10ml in terms of the original volume of the sample before concentration. The sample volume for one-time microscopy (the volume of water transferred to the chamber) shall be determined so that microscopy does not affect the viability of aquatic organisms.
 
3.4.1.4 The above procedures shall be implemented as soon as possible after sampling, at least within one day. Organisms shall be kept at the same temperature as that during the test, and no chemical fixing process shall be applied.
 
3.4.2 Counting method using morphological change and a re-growth test as criteria for judgement of viablity.
 
3.4.2.1 For organisms of the L size group, samples prepared by the procedure described in the paragraph 2.1 and 2.4 must be observed under a compound or a stereo microscope. Observe the sample under microscope. If there is any individual of which viability cannot be judged, separate that individual by sucking it out using a pipett and inoculate it into a culture medium prepared by filtering sample water using a GF/F filter. Then observe the state of recovery of appearance, mobility and re-growth for one week.
 
3.4.2.2 For organisms of the S size group, samples prepared by the procedure described in the paragraph 2.2 and 2.4 must be observed under a compound microscope. Take same steps as for organisms in L size group described above.
 
3.4.2.3 The vessel containing the medium with the inoculated aquatic organisms shall be cultivated for the same temperature conditions at the treatment, and 12 hours of bright and dark cycles (60-90 μ mol photosynthetically available radiation m-2 s-1), if necessary.
 
3.4.2.4 The inoculation of organisms for culture and observation of result of re-growth shall be completed within each one-day on the same temperature condition. The reason for such quick arrangement is to suppress changes of physiological condition of object organisms during storage.
 
Fig. 1. One of the model method for concentrating sample water
 
Fig. 2. Changes of appearance as confirmation criteria of viability
 
Fig. 3. Relationship between an individual unit cell and a colony of aquatic organisms
 
Table 1-1 Aquatic organisms (Phytoplankton) in Tokyo Bay and their minimum dimensions
mini dimension, unit: μm
No. species min max intermediate value
1 Noctiluca scintillans 150.0 2000.0 1075.0
2 Actinoptychus senarius 12.0 68.0 40.0
3 Ceratium furca 30.0 50.0 40.0
4 Thalassiosira rotula 20.0 60.0 40.0
5 Rhizosolenia fragilissima 8.0 70.0 39.0
6 Ebria tripartita 34.0 40.0 37.0
7 Detonula pumila 12.0 55.0 33.5
8 Cerataulina pelagica 7.0 56.0 31.5
9 Rhizosolenia setigera 3.0 60.0 31.5
10 Gymnodiniales 10.0 50.0 30.0
11 Gonyaulax verior 26.0 32.0 29.0
12 Distephanus speculum 15.0 35.0 25.0
13 Heterocapsa triquetra 17.0 29.0 23.0
14 Leptocylindrus mediterraneus 10.0 35.0 22.5
15 Prorocentrum minimum 15.0 23.0 19.0
16 Protoperidinium bipes 15.0 20.0 17.5
17 Skeletonema costatum 6.0 22.0 14.0
18 Eucampia zodiacus 2.5 25.0 13.8
19 Aulacoseira granulata 5.0 20.0 12.5
20 Aulacoseira distans 4.0 20.0 12.0
21 Heterosigma akashiwo 6.0 15.0 10.5
22 Chaetoceros affine - - ≒10.0
23 Chaetoceros compressum - - ≒10.0
24 Chaetoceros constrictum - - ≒10.0
25 Chaetoceros danicum - - ≒10.0
26 Chaetoceros debile - - ≒10.0
27 Chaetoceros didymum - - ≒10.0
28 Chaetoceros didymum v. anglica - - ≒10.0
29 Chaetoceros didymum v. protuberan - - ≒10.0
30 Chaetoceros lorenzianum - - ≒10.0
31 Chaetoceros radicans - - ≒10.0
32 Chaetoceros sociale - - ≒9.0
33 Cryptomonadaceae 6.0 12.0 9.0
34 Leptocylindrus danicus 6.0 12.0 9.0
35 Haptophyceae 2.0 14.0 8.0
36 Eutreptiaceae 2.5 12.5 7.5
37 Cylindrotheca closterium 1.5 8.0 4.8
38 Pseudo-nitzschia multistriata 4.0 5.0 4.5
39 Pseudo-nitzschia pungens 3.0 4.5 3.8
40 Thalassiosiraceae 2.0 5.0 3.5
41 Leptocylindrus minimus 1.5 2.5 2.0
Note: The intermediate value shall be used for computation.
 
Table 1-2 Aquatic organisms (Zooplankton) in Tokyo Bay and their minimum dimension
minimum dimension, unit: μm
No. species min max intermediate value
1 Actinopoda 50.0 10000.0 5025.0
2 Oikopleura sp. 300.0 5000.0 2650.0
3 Oikopleura dioica 500.0 1300.0 900.0
4 Podon polyphemoides 500.0 700.0 600.0
5 Nauplius larva of Copepoda 40.0 500.0 270.0
6 Sticholonche zanclea 200.0 300.0 250.0
7 Umbo larva of Bivalvia 100.0 400.0 250.0
8 Copepodite larva of Paracalanus 120.0 350.0 235.0
9 Copepodite larva of Acartia 120.0 300.0 210.0
10 Rotatoria 40.0 300.0 170.0
11 Arcella sp. 90.0 216.0 153.0
12 Copepodite larva of Oithona 100.0 200.0 150.0
13 Brachionus plicatilis 110.0 176.0 143.0
14 Oithona davisae 140.0 140.0 140.0
15 Didinium gargantua 125.0 130.0 127.5
16 Arcella vulgaris 100.0 152.0 126.0
17 Larva of Polychaeta 50.0 200.0 125.0
18 Synchaeta sp. 95.0 145.0 120.0
19 Peritrichida 38.0 200.0 119.0
20 Vorticella sp. 38.0 200.0 119.0
21 Arcella discoides 90.0 146.0 118.0
22 Tintinnidium mucicola 50.0 160.0 105.0
23 Tintinnida 15.0 167.0 91.0
24 Tintinnopsis sp. 15.0 167.0 91.0
25 Favella ehrenbergii 80.0 95.0 87.5
26 Ciliata 10.0 170.0 90.0
27 Favella taraikaensis 70.0 90.0 80.0
28 Didinium balbianii 60.0 96.0 78.0
29 D larva of Bivalvia 50.0 100.0 75.0
30 Keratella cruciformis 40.0 100.0 70.0
31 Keratella sp. 40.0 100.0 70.0
32 Oligotrichida 15.0 120.0 67.5
33 Hypotrichida 10.0 100.0 55.0
34 Tintinnopsis lohmanni 40.0 62.0 51.0
35 Euglypha sp. 30.0 60.0 45.0
36 Tintinnopsis directa 40.0 47.0 43.5
37 Amphorella quadrilineata 40.0 46.0 43.0
38 Salpingella sp. 30.0 50.0 40.0
39 Trochophora larva 40.0 40.0 40.0
40 Trichocerca sp. 28.0 50.0 39.0
41 Tintinnopsis kofoidi 35.0 38.0 36.5
42 Tintinnopsis radix 30.0 43.0 36.5
43 Eutintinnus sp. 18.0 53.0 35.5
44 Stenosemella sp. 19.0 47.0 33.0
45 Tiarina fusus 30.0 35.0 32.5
46 Tintinnopsis beroidea 25.0 40.0 32.5
47 Tintinnopsis corniger 28.0 33.0 30.5
48 Oligotrichina 10.0 50.0 30.0
49 Mesodinium rubrum 23.0 30.0 26.5
50 Tintinnopsis aperta 25.0 25.0 25.0
51 Helicostomella subulata 20.0 24.0 22.0
52 Stenosemella parvicollis 19.0 25.0 22.0
53 Nematoda 20.0 20.0 20.0
54 Helicostomella longa 17.0 18.0 17.5
Note: The intermediate value shall be used for computation.







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