The accurate determination of the offset between Mean Sea Level (MSL) and Lowest Astronomical Tide (LAT) is very important for marine and coastal navigation, mapping, and engineering (reduction of bathymetric soundings to LAT, under-keel clearance, and nearshore/offshore infrastructure levelling). The MSL value is obtained from either a local geoid model or from temporary in-situ tide gauge data processed using specialised filters. For many ungauged ports along the Gulf of Guinea, sources like Admiralty Tide Tables (ATT) provide insufficient spatial coverage, necessitating spatial interpolation from regional reference gauges. The low density, heterogeneity, and discontinuity of tide gauge observations impose the use of rigorously evaluated spatial interpolation methods. This study proposes an integrated methodological framework comparing six interpolation techniques: Nearest Neighbour (NN), Inverse-Distance Weighting (IDW), Triangulation (TIN), Spline, Trend Surface, and Kriging. The comparison is based on a regional database of 115 reference ports (106 from the ATT, and nine complementary stations from GLOSS, PSMSL, and UHSLC/JASL networks) spanning 20 West African coastal countries. Three representative Cameroonian test sites are selected: the Rio del Rey Shelf (Betika), the Wouri Estuary (Dibamba-Yassa), and the isolated southern coast (Batanga). The approach combines a unified software implementation, exhaustive comparison and leave-one-out (LOO) cross-validation (MAE, RMSE, bias, R2), convergence analysis and quadratic decomposition of uncertainty components. Results indicate that the optimal interpolation method varies with local reference station density and spatial configuration. At Betika (18 reference stations, 9 retained), IDW yields the best cross validation performance (RMSE ≈ 0.2295 m, R2 ≈ 0.1376) with Kriging close behind. At Dibamba-Yassa (06 stations, 4 retained), Trend Surface performs best (RMSE ≈ 0.1225 m, R2 ≈ 0.2833), followed by Kriging (RMSE=0.1439 m). At Batanga (2 stations only), method comparison fails, illustrating problem degeneration under extreme undersampling. In all cases, interpolation variance σᵢ² accounts for more than 95% of the total error budget, with 95% confidence intervals reaching ±3.6 m to ±4.9 m. The convergence analysis shows that a minimum of 5-7 stations is required to stabilise estimates. The main finding is that network densification is the primary lever for improvement, well ahead of algorithmic optimisation. The study provides validated point estimates for the three sites and a transparent protocol for tidal datum estimation in data sparse coastal regions of the Gulf of Guinea.
| Published in | Journal of Water Resources and Ocean Science (Volume 15, Issue 3) |
| DOI | 10.11648/j.wros.20261503.15 |
| Page(s) | 106-142 |
| Creative Commons |
This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited. |
| Copyright |
Copyright © The Author(s), 2026. Published by Science Publishing Group |
Deterministic Method, Geostatistical Method, Hydrography, LOO Cross-validation, MSL-LAT, Spatial Interpolation, Uncertainty, Vertical Reference
No. | Country | Station | (°) | (°) | (m) | 1 |
|---|---|---|---|---|---|---|
Stations from Admiralty Tide Tables | ||||||
1 | Angola | Enseada Cabinda | -5.5500 | 12.2000 | 1.10 | Micro |
2 | Angola | Soyo (Santo Ant.) | -6.1167 | 12.3667 | 1.10 | Micro |
3 | Angola | Porto de Luanda | -8.7500 | 13.2500 | 1.10 | Micro |
4 | Angola | Porto Amboim | -10.7333 | 13.7167 | 1.10 | Micro |
5 | Angola | Porto Lobito | -12.3333 | 13.5667 | 1.10 | Micro |
6 | Angola | Porto de Benguela | -12.5667 | 13.4167 | 0.92 | Micro |
7 | Angola | Baia dos Elefantes | -13.2167 | 12.7333 | 1.10 | Micro |
8 | Angola | Baia de Santa M. | -13.3500 | 12.6500 | 1.10 | Micro |
9 | Angola | Namibe | -15.2000 | 12.1500 | 1.10 | Micro |
10 | Angola | Porto Alexandre | -15.8000 | 11.8500 | 1.10 | Micro |
11 | Angola | Baia dos Tigres | -16.6000 | 11.8167 | 1.10 | Micro |
12 | Atlantic Is. | Ascension Island | -7.9167 | -14.0333 | 0.70 | Micro |
13 | Atlantic Is. | Saint Helena Is. | -15.9167 | -5.7000 | 0.50 | Micro |
14 | Benin | Cotonou | 6.3473 | 2.4105 | 0.93 | Micro |
15 | Cameroon | Rio Del Rey Ent. | 4.5000 | 8.8500 | 1.41 | Micro |
16 | Cameroon | Man O War Bay | 3.9667 | 9.3670 | 1.20 | Micro |
17 | Cameroon | Entrance Bimbia | 4.0667 | 9.1170 | 1.10 | Micro |
18 | Cameroon | Tiko-Bimbia R. | 4.0500 | 9.2170 | 1.20 | Micro |
19 | Cameroon | Cap Cameroun | 3.9000 | 9.4500 | 1.40 | Micro |
20 | Cameroon | Douala | 4.0333 | 9.7000 | 1.62 | Micro |
21 | Cameroon | Manoka | 3.9167 | 9.6000 | 1.42 | Micro |
22 | Cameroon | Malimba | 3.5333 | 9.3833 | 1.32 | Micro |
23 | Cameroon | Kribi | 2.9167 | 9.9333 | 1.00 | Micro |
24 | Congo | Pointe Noire | -4.7886 | 11.8329 | 0.96 | Micro |
25 | DR Congo | Bulabemba | -6.0500 | 12.4500 | 1.00 | Micro |
26 | Eq. Guinea | Pagalu (Annobon) | -1.4167 | 5.6333 | 0.80 | Micro |
27 | Eq. Guinea | Bata | 1.8667 | 9.7667 | 1.02 | Micro |
28 | Eq. Guinea | Rio Benito | 1.5667 | 9.6333 | 0.96 | Micro |
29 | Eq. Guinea | Cogo-Rio Muni | 1.0833 | 9.7000 | 1.49 | Micro |
30 | Eq. Guinea | Malabo | 3.7500 | 8.7833 | 1.16 | Micro |
31 | Eq. Guinea | Bahia de Luba | 3.2833 | 8.5833 | 1.02 | Micro |
32 | Gabon | Libreville | 0.3833 | 9.4500 | 1.29 | Micro |
33 | Gabon | Pointe Owendo | 0.2886 | 9.5101 | 1.45 | Micro |
34 | Gabon | Port Gentil | -0.7149 | 8.7852 | 1.45 | Micro |
35 | Gabon | Cap Esterias | 0.6167 | 9.5000 | 1.40 | Micro |
36 | Gabon | Cap Lopez | -0.6827 | 8.8580 | 1.23 | Micro |
37 | Ghana | Takoradi | 4.8869 | -1.7401 | 0.76 | Micro |
38 | Ghana | Sekondi | 4.9534 | -1.7369 | 0.98 | Micro |
39 | Ghana | Accra | 5.5599 | -0.1964 | 0.98 | Micro |
40 | Ghana | Tema | 5.6579 | 0.0260 | 0.88 | Micro |
41 | Guinea-Conakry | Rio Nunez App. | 10.6638 | -14.5844 | 2.65 | Meso |
42 | Guinea-Conakry | Port Kamsar | 10.6638 | -14.5845 | 3.03 | Meso |
43 | Guinea-Conakry | Conakry | 9.5102 | -13.7158 | 2.07 | Meso |
44 | Guinea-Bissau | Varela | 12.2865 | -16.5949 | 1.33 | Micro |
45 | Guinea-Bissau | Cacheu | 12.2746 | -16.1632 | 1.60 | Micro |
46 | Guinea-Bissau | Ilheu de Caio | 12.2794 | -16.1655 | 1.90 | Micro |
47 | Guinea-Bissau | Ponta Biombo | 11.7407 | -15.9516 | 2.33 | Meso |
48 | Guinea-Bissau | Bissau | 11.8600 | -15.5767 | 2.89 | Meso |
49 | Guinea-Bissau | Jabada | 11.9467 | -15.3477 | 3.34 | Meso |
50 | Guinea-Bissau | Porto Gole | 11.9668 | -15.1347 | 3.95 | Meso |
51 | Guinea-Bissau | Bolama | 11.5772 | -15.4798 | 2.88 | Meso |
52 | Guinea-Bissau | Sanincha | 11.8599 | -15.5767 | 2.90 | Meso |
53 | Guinea-Bissau | Bubaque | 11.3000 | -15.8272 | 2.54 | Meso |
54 | Guinea-Bissau | João Vieira | 11.1333 | -15.6318 | 2.59 | Meso |
55 | Guinea-Bissau | Cacine | 11.1318 | -15.0233 | 3.31 | Meso |
56 | Ivory Coast | Abidjan Entrance | 5.3327 | -4.0296 | 0.74 | Micro |
57 | Liberia | Monrovia | 6.3440 | -10.7930 | 0.90 | Micro |
58 | Liberia | Balfu Bay | 5.1529 | -9.2901 | 0.73 | Micro |
59 | Liberia | Sinoe Bay | 5.2901 | -8.8153 | 0.91 | Micro |
60 | Namibia | Walvis Bay | -22.9500 | 14.4833 | 0.98 | Micro |
61 | Namibia | Luderitz | -26.3167 | 15.0167 | 0.94 | Micro |
62 | Nigeria | Warri | 5.5499 | 5.7671 | 1.04 | Micro |
63 | Nigeria | Forcados River | 5.3700 | 5.4399 | 0.97 | Micro |
64 | Nigeria | Opobo River | 4.5147 | 7.5284 | 1.10 | Micro |
65 | Nigeria | Kwa Ibo River | 4.6660 | 7.9884 | 1.13 | Micro |
66 | Nigeria | Bonny Town | 4.4383 | 7.1592 | 1.48 | Micro |
67 | Nigeria | Bonny River Bar | 4.4296 | 7.1956 | 1.43 | Micro |
68 | Nigeria | No 2 Buoy | 4.3833 | 8.4000 | 1.10 | Micro |
69 | Nigeria | Bakassi Bank | 4.4500 | 8.4000 | 1.22 | Micro |
70 | Nigeria | Jamestown | 4.4833 | 8.1170 | 1.48 | Micro |
71 | Nigeria | James Island | 4.8667 | 8.1170 | 1.34 | Micro |
72 | Nigeria | Calabar | 4.9667 | 8.3170 | 2.09 | Meso |
73 | Nigeria | Inikoi Island | 4.8500 | 8.3833 | 1.60 | Micro |
74 | Nigeria | Lagos Bar | 6.5255 | 3.3785 | 0.78 | Micro |
75 | Nigeria | Badagry Creek | 6.4244 | 3.2440 | 0.61 | Micro |
76 | Nigeria | Jamestown (2) | 5.0167 | 8.3833 | 1.48 | Micro |
77 | Nigeria | James Island (2) | 5.5187 | 5.7498 | 1.54 | Micro |
78 | Nigeria | Ogidigbe | 5.5558 | 5.1822 | 0.97 | Micro |
79 | Nigeria | Forcados | 5.3456 | 5.3463 | 0.82 | Micro |
80 | Nigeria | Akassa | 4.3222 | 6.0625 | 0.98 | Micro |
81 | Nigeria | Bonny River | 4.4769 | 7.1744 | 1.48 | Micro |
82 | Nigeria | Ford Point | 4.8027 | 7.0018 | 1.52 | Micro |
83 | Nigeria | Port Harcourt | 4.8478 | 6.9650 | 1.46 | Micro |
84 | Nigeria | Sapele | 5.8964 | 5.6715 | 0.91 | Micro |
85 | Nigeria | Apapa | 6.4574 | 3.3644 | 0.88 | Micro |
86 | Nigeria | Youngtown | 4.4544 | 6.9905 | 0.59 | Micro |
87 | Nigeria | Koko | 5.9993 | 5.4460 | 0.56 | Micro |
88 | Nigeria | Madagho | 5.6019 | 5.2301 | 0.86 | Micro |
89 | Nigeria | Rugged Point | 5.5827 | 5.3727 | 0.75 | Micro |
90 | Sao Tome & Pr. | Ilha do Principe | 1.6000 | 7.2500 | 1.20 | Micro |
91 | Sao Tome & Pr. | Ilha do Sao Tome | 0.2167 | 6.7500 | 1.20 | Micro |
92 | Sierra Leone | Freetown | 8.4844 | -13.2344 | 1.77 | Micro |
93 | Sierra Leone | Shenge Point | 7.9007 | -12.9408 | 1.65 | Micro |
94 | Sierra Leone | Sheather Rock | 7.7513 | -12.7971 | 1.68 | Micro |
95 | Sierra Leone | Bonthe | 7.5312 | -12.5014 | 0.92 | Micro |
96 | South Africa | Port Nolloth | -29.2500 | 16.0833 | 1.09 | Micro |
97 | South Africa | Lamberts Bay | -32.0833 | 18.3333 | 0.85 | Micro |
98 | South Africa | Saint Helena Bay | -32.7333 | 17.8333 | 0.90 | Micro |
99 | South Africa | Saldanha | -33.0323 | 17.9214 | 0.99 | Micro |
100 | South Africa | Schrywershoek | -33.0615 | 18.0419 | 0.98 | Micro |
101 | South Africa | Cape Town | -33.9242 | 18.4127 | 0.98 | Micro |
102 | South Africa | Simons Town | -34.1929 | 18.4379 | 1.00 | Micro |
103 | South Africa | Hermanus | -34.4166 | 19.2453 | 1.02 | Micro |
104 | South Africa | Mossel Bay | -34.1837 | 22.1267 | 1.17 | Micro |
105 | South Africa | Knysna | -34.0309 | 23.0226 | 1.06 | Micro |
106 | Togo | Lome | 6.1284 | 1.2213 | 1.15 | Micro |
Complementary Stations - GLOSS / PSMSL / UHSLC2 - ATT2 | ||||||
107 | Senegal | Dakar | 14.6333 | -17.4500 | 0.82 | Micro |
108 | Mauritania | Nouakchott | 18.0830 | -15.9800 | 0.97 | Micro |
109 | Mauritania | Nouadhibou (Port-Etienne) | 20.9000 | -17.0500 | 1.00 | Micro |
110 | Gambia | Banjul | 13.4500 | -16.5700 | 1.05 | Micro |
111 | Ivory Coast | Abidjan (GLOSS) | 5.2500 | -4.2500 | 0.74 | Micro |
112 | Cameroon | Port Sonara (Limbe) | 4.0050 | 9.1250 | 1.20 | Micro |
113 | Congo | Pointe Noire (GLOSS) | -4.7830 | 11.8330 | 0.96 | Micro |
114 | Sao Tome & Pr. | Sao Tome (PSMSL) | 0.0167 | 6.5167 | 1.20 | Micro |
115 | Cape Verde | Palmeira (Sal) | 16.7550 | -22.9300 | 0.65 | Micro |
Parameter | Dibamba-Yassa | Betika | Batanga |
|---|---|---|---|
Geographic Coord. (WGS84) | Lat=03°56'26" N | Lat=04°16'27" N | Lat=02°48'48" N |
Lon=009°49'14" E | Lon=008°23'07" E | Lon=009°49'00" E | |
Water Depth (LAT) | 5.0 m | 21.5 m | 30.0 m |
Model | Variogram formula |
|---|---|
Spherical |
|
Exponential |
|
Gaussian |
|
Matern 3/2 |
|
Matern 5/2 |
|
Metric | Formula | Interpretation |
|---|---|---|
MAE |
| Mean Absolute Error: mean absolute deviation between observed and estimated values. |
RMSE |
| Root Mean Square Error: strongly penalises large and outlying errors. |
R² |
| Coefficient of Determination: proportion of variance explained (Z̄=mean of observations). |
Bias |
| Systematic Bias: tendency to consistently under- or over-estimate values. |
Parameter | Value |
|---|---|
Available stations (100 km radius) | 18 |
Retained stations (CV | 9 |
Inter-station distances (km) | 12.2 - 133.0 (mean ≈ 78.3) |
Spatial extent (lat × lon) | ≈ 1.73° × 2.25° |
Spatial variance σ² (m²) | 0.0611 (σ ≈ 0.25 m; CV=18.8%) |
Station density / 1,000 km² | 0.347 |
Mean MSL-LAT of 18 stations (m) | 1.31 |
MSL-LAT range (m) | 1.02 (Bahia de Luba) - 2.09 (Calabar) |
Rank | Method | Score | σₜ (m) | Level |
|---|---|---|---|---|
1 | IDW | 0.370 | ±2.479 | AccepTable |
2 | Kriging | 0.358 | ±2.479 | AccepTable |
3 | TIN | 0.219 | ±2.483 | Limited |
4 | Trend | 0.069 | ±2.488 | Limited |
5 | NN | -0.125 | ±2.493 | Limited |
6 | Spline | -0.149 | ±2.494 | Limited |
Method | NN | IDW | TIN | Trend | Spline | Kriging |
|---|---|---|---|---|---|---|
NN | 1.000 | 0.893 | 0.896 | 0.722 | 0.923 | 0.712 |
IDW | 0.893 | 1.000 | 0.768 | 0.837 | 0.890 | 0.785 |
TIN | 0.896 | 0.768 | 1.000 | 0.692 | 0.815 | 0.721 |
Trend | 0.722 | 0.837 | 0.692 | 1.000 | 0.845 | 0.597 |
Spline | 0.923 | 0.890 | 0.815 | 0.845 | 1.000 | 0.640 |
Kriging | 0.712 | 0.785 | 0.721 | 0.597 | 0.640 | 1.000 |
Component | Value (m²) | Share in σt² (%) |
|---|---|---|
σᵢ² (interpolation variance, spatial configure) | 6.0827 | ≈ 96% |
σd² (data source quality -IDW) | 0.0527 | ≈ 1% |
σd² (data source quality -NN) | 0.1225 | (reference) |
σm² (model specification -all methods) | 0.0098 | < 1% |
σt (IDW) | ±2.479 m | - |
CI₉₅ (IDW) | ±4.859 m | - |
Parameter | Value |
|---|---|
Available stations (68 km radius) | 6 |
Minimum inter-station distance (km) | 11.8 |
Maximum inter-station distance (km) | 65.8 |
Mean inter-station distance (km) | 37.0 |
Spatial extent (lat × lon) | ≈ 0.52° × 0.48° |
Spatial variance σ² (m²) | 0.0209 (σ ≈ 0.145 m; CV=10.6%) |
Station density / 1,000 km² | 1.766 |
Mean MSL-LAT of 6 stations (m) | 1.36 |
MSL-LAT range (m) | 1.20 (Tiko-Bimbia River) - 1.62 (Douala) |
Rank | Method | Score | σₜ (m) | Level |
|---|---|---|---|---|
1 | Trend | 0.539 | ±2.117 | Good |
2 | Kriging | 0.431 | ±2.118 | AccepTable |
3 | NN | 0.423 | ±2.119 | AccepTable |
4 | TIN | 0.352 | ±2.119 | AccepTable |
5 | Spline | 0.245 | ±2.121 | Limited |
6 | IDW | 0.224 | ±2.121 | Limited |
Method | NN | IDW | TIN | Trend | Spline | Kriging |
|---|---|---|---|---|---|---|
NN | 1.000 | 0.624 | 0.512 | 0.830 | 0.780 | 0.654 |
IDW | 0.624 | 1.000 | 0.959 | 0.695 | 0.681 | 0.972 |
TIN | 0.512 | 0.959 | 1.000 | 0.709 | 0.701 | 0.978 |
Trend | 0.830 | 0.695 | 0.709 | 1.000 | 0.988 | 0.813 |
Spline | 0.780 | 0.681 | 0.701 | 0.988 | 1.000 | 0.810 |
Kriging | 0.654 | 0.972 | 0.978 | 0.813 | 0.810 | 1.000 |
Component | Value (m²) | Share in σₜ² (%) |
|---|---|---|
σᵢ² (interpolation variance, spatial configure) | 4.4610 | > 95% |
σd² (data quality - Trend Surface) | 0.0150 | ≈ 1% |
σd² (data quality - NN) | 0.0211 | (reference) |
σm² (model specification - all methods) | 0.0058 | < 1% |
σₜ (Trend Surface, 6 stations) | ±2.117 m | - |
CI₉₅ (Trend Surface, 6 stations) | ±4.149 m | - |
σₜ (Trend Surface, dedicated validation - 4 stations) | ±1.834 m | - |
CI₉₅ (Trend Surface, dedicated validation) | ±3.595 m | - |
Parameter | Value |
|---|---|
Number of available stations | 2 (Kribi and Malimba) |
Distances to site (km) | 17.3 (Kribi, south); 93.4 (Malimba, north) |
Mean distance to site (km) | 55.4 |
Spatial extent (lat × lon) | ≈ 0.62° × 0.55° |
MSL-LAT of stations (m) | 1.00 (Kribi); 1.32 (Malimba) |
Spatial variance σ² (m²) | ≈ 0.0256 (n=2, statistically non-significant) |
Station density / 1,000 km² | ≈ 0.302 |
Coefficient of variation CV (%) | 13.8 (uninterpreTable with n=2) |
Rank | Method | Score | σₜ (m) | Level |
|---|---|---|---|---|
1-6 | All methods | -0.716 | ±2.375 | Unusable |
Component | Value (m²) | Share in σₜ² (%) |
|---|---|---|
σᵢ² (interpolation variance) | 5.5826 | > 98% |
σd² (data source quality -NN) | 0.1447 | ≈ 2% |
σm² (model specification) | 0.0032 | < 0.1% |
σₜ | ±2.375 m | - |
CI₉₅ | ±4.662 m | - |
Parameter | Dibamba-Yassa | Betika | Batanga |
|---|---|---|---|
Context | Wouri Estuary (<20 m) | Rio del Rey Shelf (20-50 m) | Isolated open coast |
Available / retained stations | 6 / 4 | 18 / 9 | 2 / 2 |
Distance range (km) | 16.9 - 50.4 | 12.2 - 133.0 | 17.3 - 93.4 |
Spatial extent (lat × lon) | ≈ 0.52° × 0.48° | ≈ 1.73° × 2.25° | ≈ 0.62° × 0.55° |
Density (st./1,000 km²) | 1.766 | 0.347 | 0.302 |
Spatial σ (m) / CV (%) | 0.145 / 10.6 | 0.25 / 18.8 | 0.16 / 13.8 (n.s.) |
Retained method | Trend Surface (kopt=4) | IDW (kopt=9) | NN (default, kopt=1)) |
MSL-LAT offset (m) | 1.571 | 1.147 | 1.00 |
Best RMSE (m) | 0.1225 (Trend) | 0.2295 (IDW) | 0.320 (all) |
Best R² | 0.2833 (Trend) | 0.1376 (IDW) | -3.000 (all) |
σₜ / CI₉₅ (m) | ±1.834 / ±3.595 | ±2.479 / ±4.859 | ±2.375 / ±4.662 |
Performance level | Good | AccepTable (moderate) | Unusable |
Relative confidence (0-3) | 2 | 1-2 | 0 |
Rank | Dibamba-Yassa (RMSE, m) | Betika (RMSE, m) | Batanga (RMSE, m) |
|---|---|---|---|
1 | Trend (0.1225) | IDW (0.2295) | All (0.320) |
2 | Kriging (0.1439) | Kriging (0.2343) | - |
3 | NN (0.1454) | TIN (0.2706) | - |
4 | TIN (0.1571) | Trend (0.3095) | - |
5 | Spline (0.1746) | NN (0.3501) | - |
6 | IDW (0.1777) | Spline (0.3562) | - |
RMSE range | 0.1225 - 0.1777 (0.055 m) | 0.2295 - 0.3562 (0.127 m) | 0 (degeneration) |
Site | σᵢ² (m²) | σd² (m²) | σm² (m²) | σₜ (m) | Share σᵢ² (%) |
|---|---|---|---|---|---|
Dibamba-Yassa (4 st.) | 4.4610 | 0.015 - 0.032 | 0.006 | ±1.834 | > 95% |
Betika (9 st.) | 6.0827 | 0.053 - 0.123 | 0.010 | ±2.479 | ≈ 96% |
Batanga (2 st.) | 5.5826 | 0.145 | 0.003 | ±2.375 | > 98% |
Site | Context | Reliability | Operational Recommendation |
|---|---|---|---|
Dibamba-Yassa | Complex estuary (<20 m) | Good | Trend Surface suitable for operational use. In-situ validation by temporary tide gauge (≥15 days) recommended for critical applications. |
Betika | Shelf (20-50 m) | Moderate to accepTable | Offshore surveys with conservative vertical margin ≈ ±4.9 m. Densify network to south of site. |
Batanga | Isolated open coast | None | Use discouraged without dedicated tide gauge campaign. Nearest station value for indicative use only. |
Density / Context | Preferred Method | kopt | Typical RMSE | Operational CI₉₅ |
|---|---|---|---|---|
≥5-7 stations, extent >1° (Betika, Nigeria/Cameroon clusters) | 1-IDW, 2-Kriging, 3-TIN | 6-10 | 0.22-0.29 m | ±4.9 m; conservative margins |
2-6 stations, extent <0.7° (Dibamba-Yassa, estuaries) | 1-Trend, 2-Kriging, 3-NN | 2-4 | 0.12-0.15 m | ±3.6 m; in-situ validation required |
<3 stations, isolated coast (Batanga, Angola, Guinea) | NN (nearest station) | 1 | 0.32 m | Invalidate; tide gauge campaign required |
ATT | Admiralty Tide Tables |
BLUE | Best Linear Unbiased Estimator |
CI | Confidence Interval |
GCV | Generalised Cross-Validation |
GLOSS | Global Sea Level Observing System |
IDW | Inverse-Distance Weighting |
IHO | International Hydrographic Organization |
JASL | Joint Archive for Sea Level |
LAT | Lowest Astronomical Tide |
LOO | Leave-One-Out |
LOOCV | Leave-One-Out Cross-Validation |
MAE | Mean Absolute Error |
MSL | Mean Sea Level |
NN | Nearest Neighbour |
PSMSL | Permanent Service for Mean Sea Level |
RMSE | Root Mean Square Error |
TCARI | Tidal Constituent and Residual Interpolation |
TIN | Triangulated Irregular Network |
TPS | Thin-Plate Spline |
UHSLC | University of Hawaii Sea Level Center |
UTM | Universal Transverse Mercator |
WGS84 | World Geodetic System 1984 |
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APA Style
Mfeze, M. (2026). Spatial Interpolation of Hydrographic Vertical References in the Gulf of Guinea: Hierarchical Ranking of Geostatistical and Deterministic Methods by LOO Cross-validation. Journal of Water Resources and Ocean Science, 15(3), 106-142. https://doi.org/10.11648/j.wros.20261503.15
ACS Style
Mfeze, M. Spatial Interpolation of Hydrographic Vertical References in the Gulf of Guinea: Hierarchical Ranking of Geostatistical and Deterministic Methods by LOO Cross-validation. J. Water Resour. Ocean Sci. 2026, 15(3), 106-142. doi: 10.11648/j.wros.20261503.15
@article{10.11648/j.wros.20261503.15,
author = {Michel Mfeze},
title = {Spatial Interpolation of Hydrographic Vertical References in the Gulf of Guinea: Hierarchical Ranking of Geostatistical and Deterministic Methods by LOO Cross-validation},
journal = {Journal of Water Resources and Ocean Science},
volume = {15},
number = {3},
pages = {106-142},
doi = {10.11648/j.wros.20261503.15},
url = {https://doi.org/10.11648/j.wros.20261503.15},
eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.wros.20261503.15},
abstract = {The accurate determination of the offset between Mean Sea Level (MSL) and Lowest Astronomical Tide (LAT) is very important for marine and coastal navigation, mapping, and engineering (reduction of bathymetric soundings to LAT, under-keel clearance, and nearshore/offshore infrastructure levelling). The MSL value is obtained from either a local geoid model or from temporary in-situ tide gauge data processed using specialised filters. For many ungauged ports along the Gulf of Guinea, sources like Admiralty Tide Tables (ATT) provide insufficient spatial coverage, necessitating spatial interpolation from regional reference gauges. The low density, heterogeneity, and discontinuity of tide gauge observations impose the use of rigorously evaluated spatial interpolation methods. This study proposes an integrated methodological framework comparing six interpolation techniques: Nearest Neighbour (NN), Inverse-Distance Weighting (IDW), Triangulation (TIN), Spline, Trend Surface, and Kriging. The comparison is based on a regional database of 115 reference ports (106 from the ATT, and nine complementary stations from GLOSS, PSMSL, and UHSLC/JASL networks) spanning 20 West African coastal countries. Three representative Cameroonian test sites are selected: the Rio del Rey Shelf (Betika), the Wouri Estuary (Dibamba-Yassa), and the isolated southern coast (Batanga). The approach combines a unified software implementation, exhaustive comparison and leave-one-out (LOO) cross-validation (MAE, RMSE, bias, R2), convergence analysis and quadratic decomposition of uncertainty components. Results indicate that the optimal interpolation method varies with local reference station density and spatial configuration. At Betika (18 reference stations, 9 retained), IDW yields the best cross validation performance (RMSE ≈ 0.2295 m, R2 ≈ 0.1376) with Kriging close behind. At Dibamba-Yassa (06 stations, 4 retained), Trend Surface performs best (RMSE ≈ 0.1225 m, R2 ≈ 0.2833), followed by Kriging (RMSE=0.1439 m). At Batanga (2 stations only), method comparison fails, illustrating problem degeneration under extreme undersampling. In all cases, interpolation variance σᵢ² accounts for more than 95% of the total error budget, with 95% confidence intervals reaching ±3.6 m to ±4.9 m. The convergence analysis shows that a minimum of 5-7 stations is required to stabilise estimates. The main finding is that network densification is the primary lever for improvement, well ahead of algorithmic optimisation. The study provides validated point estimates for the three sites and a transparent protocol for tidal datum estimation in data sparse coastal regions of the Gulf of Guinea.},
year = {2026}
}
TY - JOUR T1 - Spatial Interpolation of Hydrographic Vertical References in the Gulf of Guinea: Hierarchical Ranking of Geostatistical and Deterministic Methods by LOO Cross-validation AU - Michel Mfeze Y1 - 2026/06/30 PY - 2026 N1 - https://doi.org/10.11648/j.wros.20261503.15 DO - 10.11648/j.wros.20261503.15 T2 - Journal of Water Resources and Ocean Science JF - Journal of Water Resources and Ocean Science JO - Journal of Water Resources and Ocean Science SP - 106 EP - 142 PB - Science Publishing Group SN - 2328-7993 UR - https://doi.org/10.11648/j.wros.20261503.15 AB - The accurate determination of the offset between Mean Sea Level (MSL) and Lowest Astronomical Tide (LAT) is very important for marine and coastal navigation, mapping, and engineering (reduction of bathymetric soundings to LAT, under-keel clearance, and nearshore/offshore infrastructure levelling). The MSL value is obtained from either a local geoid model or from temporary in-situ tide gauge data processed using specialised filters. For many ungauged ports along the Gulf of Guinea, sources like Admiralty Tide Tables (ATT) provide insufficient spatial coverage, necessitating spatial interpolation from regional reference gauges. The low density, heterogeneity, and discontinuity of tide gauge observations impose the use of rigorously evaluated spatial interpolation methods. This study proposes an integrated methodological framework comparing six interpolation techniques: Nearest Neighbour (NN), Inverse-Distance Weighting (IDW), Triangulation (TIN), Spline, Trend Surface, and Kriging. The comparison is based on a regional database of 115 reference ports (106 from the ATT, and nine complementary stations from GLOSS, PSMSL, and UHSLC/JASL networks) spanning 20 West African coastal countries. Three representative Cameroonian test sites are selected: the Rio del Rey Shelf (Betika), the Wouri Estuary (Dibamba-Yassa), and the isolated southern coast (Batanga). The approach combines a unified software implementation, exhaustive comparison and leave-one-out (LOO) cross-validation (MAE, RMSE, bias, R2), convergence analysis and quadratic decomposition of uncertainty components. Results indicate that the optimal interpolation method varies with local reference station density and spatial configuration. At Betika (18 reference stations, 9 retained), IDW yields the best cross validation performance (RMSE ≈ 0.2295 m, R2 ≈ 0.1376) with Kriging close behind. At Dibamba-Yassa (06 stations, 4 retained), Trend Surface performs best (RMSE ≈ 0.1225 m, R2 ≈ 0.2833), followed by Kriging (RMSE=0.1439 m). At Batanga (2 stations only), method comparison fails, illustrating problem degeneration under extreme undersampling. In all cases, interpolation variance σᵢ² accounts for more than 95% of the total error budget, with 95% confidence intervals reaching ±3.6 m to ±4.9 m. The convergence analysis shows that a minimum of 5-7 stations is required to stabilise estimates. The main finding is that network densification is the primary lever for improvement, well ahead of algorithmic optimisation. The study provides validated point estimates for the three sites and a transparent protocol for tidal datum estimation in data sparse coastal regions of the Gulf of Guinea. VL - 15 IS - 3 ER -