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cluster_id
int64
patch_id
string
wc_mode_label
string
cluster_size
int64
n_labels
int64
0
S2A_MSIL2A_20240927T083731_R064_T36RUU_20240927T130851_892_2406_6842
Built-up
2
2
0
S2B_MSIL2A_20241007T175129_R141_T12RWS_20241007T213533_6930_5846_40e2
Shrubland
2
2
1
S2B_MSIL2A_20240404T072609_R049_T38RPV_20240404T134340_10450_394_ba2d
Built-up
2
2
1
S2B_MSIL2A_20240721T082609_R021_T36SWG_20240721T122007_6578_5174_23ff
Grassland
2
2
2
S2B_MSIL2A_20241114T052959_R105_T43RGM_20241114T075133_1348_10232_74d0
Cropland
3
2
2
S2B_MSIL2A_20241114T052959_R105_T43RGM_20241114T075133_8850_6472_5ca4
Cropland
3
2
2
S2B_MSIL2A_20240723T072619_R049_T38RQV_20240723T101745_4314_10654_99b1
Permanent water
3
2
3
S2A_MSIL2A_20240903T171901_R012_T14TNK_20240904T003950_6162_1866_c86a
Cropland
2
2
3
S2A_MSIL2A_20240412T155901_R097_T17RMJ_20240413T001531_8610_5046_9bd5
Herbaceous wetland
2
2
4
S2A_MSIL2A_20240903T171901_R012_T14TPK_20240904T003950_10294_4578_a73f
Cropland
2
2
4
S2A_MSIL2A_20240709T220531_R072_T06WVD_20240710T031937_2198_10654_b1f6
Herbaceous wetland
2
2
5
S2A_MSIL2A_20240903T171901_R012_T14TPK_20240904T003950_6728_5192_b0c3
Cropland
4
2
5
S2A_MSIL2A_20240903T171901_R012_T14TNL_20240904T003950_6788_8524_729d
Cropland
4
2
5
S2A_MSIL2A_20240705T172001_R012_T14TNL_20240706T045514_9252_2114_207a
Cropland
4
2
5
S2A_MSIL2A_20240622T084601_R107_T36UVV_20240622T131254_9760_4848_ed0b
Permanent water
4
2
6
S2A_MSIL2A_20240903T171901_R012_T14TNL_20240904T003950_7734_7256_eed8
Cropland
2
2
6
S2A_MSIL2A_20240622T084601_R107_T36UVV_20240622T131254_9238_3830_c088
Permanent water
2
2
7
S2A_MSIL2A_20240605T171901_R012_T14SNH_20240606T022358_3992_9364_6ead
Cropland
2
2
7
S2B_MSIL2A_20240824T133149_R081_T23LKF_20240824T154650_5590_9240_4b10
Shrubland
2
2
8
S2A_MSIL2A_20240605T171901_R012_T14SNH_20240606T022358_7744_1912_ec3d
Cropland
2
2
8
S2A_MSIL2A_20240709T220531_R072_T06WVD_20240710T031937_1398_8812_a32c
Herbaceous wetland
2
2
9
S2B_MSIL2A_20240819T171859_R012_T14TPK_20240819T214314_3254_2306_6547
Cropland
2
2
9
S2B_MSIL2A_20240404T072609_R049_T38RPV_20240404T134340_9370_9308_f584
Permanent water
2
2
10
S2B_MSIL2A_20240819T171859_R012_T14TPK_20240819T214314_216_4146_348b
Cropland
3
3
10
S2B_MSIL2A_20240227T160129_R097_T17RMK_20240227T221324_9006_1832_b563
Herbaceous wetland
3
3
10
S2A_MSIL2A_20240210T170441_R069_T14QMG_20240211T150932_1768_4870_eec6
Permanent water
3
3
11
S2B_MSIL2A_20240819T171859_R012_T14TPK_20240819T214314_1656_666_bff2
Cropland
2
2
11
S2B_MSIL2A_20240730T071619_R006_T42WWD_20240730T083338_9038_5788_e012
Permanent water
2
2
12
S2A_MSIL2A_20240705T172001_R012_T14TNL_20240706T045514_10650_6912_ec57
Cropland
2
2
12
S2B_MSIL2A_20250120T135659_R067_T20HNF_20250120T192956_5046_8294_282e
Permanent water
2
2
13
S2B_MSIL2A_20240705T080609_R078_T37TEL_20240706T023152_7906_10194_0db2
Cropland
2
2
13
S2B_MSIL2A_20240721T082609_R021_T36SWG_20240721T122007_1124_6674_abec
Grassland
2
2
14
S2C_MSIL2A_20250208T133901_R124_T22JBP_20250208T164510_5686_6816_5cf9
Cropland
2
2
14
S2A_MSIL2A_20241121T043101_R133_T45QZE_20241121T074250_7090_3982_7e53
Mangroves
2
2
15
S2B_MSIL2A_20240826T170849_R112_T15STD_20240826T212041_10016_652_3f37
Cropland
2
2
15
S2A_MSIL2A_20240922T074631_R135_T36MYD_20240922T111958_8816_9170_9614
Shrubland
2
2
16
S2A_MSIL2A_20240610T150731_R082_T18LYL_20240610T220607_278_9352_d87a
Grassland
2
2
16
S2B_MSIL2A_20240715T133149_R081_T23LKE_20240715T173436_2380_4384_1657
Shrubland
2
2
17
S2A_MSIL2A_20240624T012721_R131_T53LKF_20240624T073349_4126_6990_4c0c
Grassland
3
2
17
S2B_MSIL2A_20240824T133149_R081_T23LKF_20240824T154650_4888_6492_dbad
Shrubland
3
2
17
S2A_MSIL2A_20240922T175041_R141_T12RWR_20240922T232752_5724_528_a633
Shrubland
3
2
18
S2B_MSIL2A_20250119T142709_R053_T19GDN_20250119T194952_1586_4492_d5e2
Grassland
2
2
18
S2B_MSIL2A_20240708T081609_R121_T34KGD_20240712T101848_1266_7624_de26
Herbaceous wetland
2
2
19
S2B_MSIL2A_20240730T071619_R006_T42WWD_20240730T083338_1432_5108_96d8
Grassland
2
2
19
S2B_MSIL2A_20240907T174909_R141_T12RWR_20240907T215349_7340_1256_96f4
Shrubland
2
2
20
S2A_MSIL2A_20240829T131251_R081_T27WWM_20240829T155457_5174_9036_18be
Grassland
4
2
20
S2A_MSIL2A_20240824T035531_R004_T48TWT_20240824T103901_9846_4374_84c2
Grassland
4
2
20
S2A_MSIL2A_20240824T035531_R004_T48TWT_20240824T103901_9222_5526_0834
Grassland
4
2
20
S2A_MSIL2A_20240729T140051_R067_T21KVA_20240729T232452_9722_5920_f262
Herbaceous wetland
4
2
21
S2B_MSIL2A_20240227T160129_R097_T17RMK_20240227T221324_6338_4304_f87b
Grassland
2
2
21
S2B_MSIL2A_20240922T135659_R067_T21KWA_20240922T194135_2840_800_2f51
Herbaceous wetland
2
2
22
S2A_MSIL2A_20240720T213531_R086_T05WPM_20240721T035033_1614_5718_f684
Grassland
4
2
22
S2B_MSIL2A_20240826T170849_R112_T15STD_20240826T212041_8286_4542_890c
Grassland
4
2
22
S2B_MSIL2A_20250116T054059_R005_T42QZF_20250116T074800_8378_2744_9d93
Permanent water
4
2
22
S2B_MSIL2A_20250116T054059_R005_T42QZF_20250116T074800_8360_3460_1a39
Permanent water
4
2
23
S2A_MSIL2A_20240720T213531_R086_T05WPM_20240721T035033_4464_4924_381e
Grassland
2
2
23
S2A_MSIL2A_20240922T175041_R141_T12RWR_20240922T232752_4400_5858_535c
Mangroves
2
2
24
S2A_MSIL2A_20240903T171901_R012_T14TNL_20240904T003950_6708_2568_b9e2
Grassland
2
2
24
S2A_MSIL2A_20240412T155901_R097_T17RMJ_20240413T001531_9918_5780_8d2e
Herbaceous wetland
2
2
25
S2B_MSIL2A_20241102T001109_R073_T55HFC_20241102T013455_4596_1010_1d7d
Grassland
2
2
25
S2A_MSIL2A_20240922T175041_R141_T12RWR_20240922T232752_10246_1392_e1ca
Shrubland
2
2
26
S2A_MSIL2A_20240824T035531_R004_T48TWT_20240824T103901_8388_4984_850a
Grassland
2
2
26
S2A_MSIL2A_20240818T135701_R067_T21KVA_20240818T212251_4386_1144_7484
Herbaceous wetland
2
2
27
S2C_MSIL2A_20250205T150751_R082_T19NDG_20250205T181611_10130_2540_d155
Grassland
2
2
27
S2A_MSIL2A_20240709T220531_R072_T06WVD_20240710T031937_1332_8210_d1be
Herbaceous wetland
2
2
28
S2C_MSIL2A_20250205T150751_R082_T19NDG_20250205T181611_2030_10800_095e
Grassland
2
2
28
S2B_MSIL2A_20240801T125709_R038_T33XWG_20240801T165443_1640_4964_6d93
Herbaceous wetland
2
2
29
S2C_MSIL2A_20250205T150751_R082_T19NDG_20250205T181611_10260_6044_3d1c
Grassland
2
2
29
S2A_MSIL2A_20240709T220531_R072_T06WVD_20240710T031937_3820_10670_fd76
Herbaceous wetland
2
2
30
S2C_MSIL2A_20250205T150751_R082_T19NDG_20250205T181611_8418_6924_4f37
Grassland
2
2
30
S2A_MSIL2A_20250112T083321_R021_T36RTV_20250112T131250_10084_2072_46aa
Herbaceous wetland
2
2
31
S2B_MSIL2A_20240902T135709_R067_T21KWA_20240902T180147_6494_876_e80e
Herbaceous wetland
2
2
31
S2B_MSIL2A_20240831T132239_R038_T23LLE_20240831T152654_4112_7724_44b6
Tree cover
2
2
32
S2B_MSIL2A_20240902T135709_R067_T21KWA_20240902T180147_8182_1710_1189
Herbaceous wetland
2
2
32
S2A_MSIL2A_20241012T175301_R141_T12RWR_20241012T232550_6806_234_c473
Shrubland
2
2
33
S2A_MSIL2A_20240818T135701_R067_T21KVA_20240818T212251_5804_8544_977f
Herbaceous wetland
2
2
33
S2C_MSIL2A_20250207T053031_R105_T43QBB_20250207T084610_9942_10944_a23c
Tree cover
2
2
34
S2A_MSIL2A_20240818T135701_R067_T21KVA_20240818T212251_4258_2088_b775
Herbaceous wetland
2
2
34
S2C_MSIL2A_20250205T150751_R082_T19NDG_20250205T181611_2272_156_88e0
Shrubland
2
2
35
S2A_MSIL2A_20240729T140051_R067_T21KVA_20240729T232452_8152_7352_d37c
Herbaceous wetland
2
2
35
S2A_MSIL2A_20240316T074651_R135_T36MYA_20240316T124705_4284_1360_f07f
Shrubland
2
2
36
S2A_MSIL2A_20240729T140051_R067_T21KVA_20240729T232452_4538_22_ab4b
Herbaceous wetland
2
2
36
S2A_MSIL2A_20240415T110621_R137_T29SQD_20240415T192129_6758_4576_b97d
Tree cover
2
2
37
S2A_MSIL2A_20240512T155901_R097_T17RMJ_20240513T012444_10636_2142_44b7
Herbaceous wetland
2
2
37
S2A_MSIL2A_20240721T023551_R089_T49MDM_20240721T065350_4278_8262_c52a
Tree cover
2
2
38
S2A_MSIL2A_20240512T155901_R097_T17RMJ_20240513T012444_9248_5072_f72d
Herbaceous wetland
2
2
38
S2A_MSIL2A_20240922T074631_R135_T36MYD_20240922T111958_5552_2800_a77a
Shrubland
2
2
39
S2A_MSIL2A_20240709T220531_R072_T06WVD_20240710T031937_4504_10632_e09f
Herbaceous wetland
2
2
39
S2B_MSIL2A_20240715T133149_R081_T23LKE_20240715T173436_486_2712_0813
Shrubland
2
2
40
S2B_MSIL2A_20240720T071619_R006_T42WWD_20240720T100731_7978_9584_6ef8
Herbaceous wetland
2
2
40
S2B_MSIL2A_20241115T082119_R121_T34HCH_20241115T111328_7884_3298_4e9b
Shrubland
2
2
41
S2A_MSIL2A_20241130T100351_R122_T31NEH_20241130T132849_812_9084_4354
Mangroves
2
2
41
S2A_MSIL2A_20240316T074651_R135_T36MYA_20240316T124705_6142_3336_f33c
Shrubland
2
2
42
S2B_MSIL2A_20241126T043029_R133_T45QYE_20241126T064312_5074_4976_c4b2
Mangroves
3
2
42
S2B_MSIL2A_20250116T054059_R005_T42QZF_20250116T074800_8840_2500_2590
Permanent water
3
2
42
S2B_MSIL2A_20250116T054059_R005_T42QZF_20250116T074800_8580_3904_3950
Permanent water
3
2
43
S2B_MSIL2A_20241126T043029_R133_T45QYE_20241126T064312_9284_4112_e2e3
Mangroves
3
2
43
S2B_MSIL2A_20241126T043029_R133_T45QYE_20241126T064312_4524_4430_75af
Mangroves
3
2
43
S2B_MSIL2A_20250116T054059_R005_T42QZF_20250116T074800_10626_6226_d164
Permanent water
3
2
44
S2B_MSIL2A_20241126T043029_R133_T45QYE_20241126T064312_7648_8738_ecb7
Mangroves
2
2
End of preview. Expand in Data Studio

Similar But Different — Sentinel-2 patches with deceptive RGB

30,927 32×32 Sentinel-2 L2A multispectral patches (12 bands resampled to 10 m) across ten ESA WorldCover classes, selected so that the visible bands are uninformative by construction: every patch sits in a region of RGB-mean space dominated by patches of other classes, while its NIR / red-edge / SWIR response stays class-informative.

The dataset is a controlled probe for one question: does a model actually use the bands outside the visible range? On most land-cover benchmarks an RGB-only model nearly matches a full multispectral model, so band ablations have no leverage. Here an RGB-only ResNet-18 reaches 0.71 test accuracy while the same model with all 12 bands reaches 0.82 — and frozen multispectral foundation-model probes reach 0.87. See the announcement post at https://geospatialml.com/posts/similar-but-different/ for full benchmarks.

How it was built

Imagery is Sentinel-2 L2A from the Microsoft Planetary Computer; labels come from ESA WorldCover 10 m 2021 v200.

  1. Candidate sampling. Random 32×32 windows from Sentinel-2 L2A scenes (scene-level cloud cover < 10%) at 200 hand-picked locations spread across continents, biomes, and seasons; windows containing cloud or shadow pixels (per the SCL band) are discarded. This yields 397,839 patches from 5,292 scenes, with per-channel RGB means and standard deviations computed on the 8-bit visual (true-colour) asset.
  2. Spectral-difference filtering. Find all patch pairs whose RGB-mean vectors are within Euclidean distance 2.0 and whose RGB-std vectors are within distance 3.0 (so pairs match in texture, not just average colour). For those candidates, fetch the NIR band (B08) and keep pairs whose B08 means differ by a large margin — every surviving patch has at least one RGB look-alike with a very different NIR response.
  3. Full bands + labels. Download all 12 L2A surface-reflectance bands for surviving patches (20 m / 60 m bands resampled to 10 m, bilinear) and label each patch with the mode WorldCover class over its footprint, keeping the full per-class percentage distribution.
  4. RGB-ambiguity selection. Restrict to patches ≥ 70% a single WorldCover class that participate in a pair with |ΔB08| > 1000 (uint16 surface reflectance), then compute each patch's k = 20 nearest neighbours in (R̄, Ḡ, B̄) space and keep the patch only if ≥ 18 of its 20 RGB-mean neighbours carry a different label. A k-NN / nearest-centroid classifier on RGB means is therefore wrong on these patches by construction. Snow and ice survived with too few patches to split and was dropped, leaving ten classes and 30,927 patches.

What's in this repo

similar-but-different/
├── README.md                       # this file
├── splits.json                     # scene-disjoint 80/10/10 train/val/test
├── landcover_distribution.parquet  # per-patch WorldCover percentages
├── eval/
│   ├── test_pairs.parquet          # RGB-similar / NIR-different test pairs
│   └── test_hard_clusters.parquet  # RGB-confusable, multi-class test clusters
└── shards/
    ├── Bare_sparse_veg.parquet     # one parquet shard per class
    ├── Built-up.parquet
    ├── Cropland.parquet
    ├── Grassland.parquet
    ├── Herbaceous_wetland.parquet
    ├── Mangroves.parquet
    ├── Moss_and_lichen.parquet
    ├── Permanent_water.parquet
    ├── Shrubland.parquet
    └── Tree_cover.parquet

Each shard row holds one patch: the complete GeoTIFF as tif bytes plus metadata columns (patch_id, scene_id, wc_mode_class, wc_mode_label, wc_mode_pct, wc_n_valid, and wc_class_<code>_pct for the full WorldCover distribution over the patch footprint).

Each embedded GeoTIFF is a 12-band uint16 raster, 32×32 px at 10 m, georeferenced in the source scene's UTM CRS (nodata=0, compress=deflate). Values are L2A surface reflectance (divide by 10,000 for reflectance in [0, 1]). GeoTIFF tags carry patch_id, scene_id, wc_mode_label, wc_mode_pct, and the patch centre in UTM coordinates; per-band descriptions name each band.

Band order

# Band Wavelength (nm) Native res (m)
1 B01 (coastal aerosol) 443 60
2 B02 (blue) 490 10
3 B03 (green) 560 10
4 B04 (red) 665 10
5 B05 (red edge 1) 705 20
6 B06 (red edge 2) 740 20
7 B07 (red edge 3) 783 20
8 B08 (NIR) 842 10
9 B8A (narrow NIR) 865 20
10 B09 (water vapour) 945 60
11 B11 (SWIR 1) 1610 20
12 B12 (SWIR 2) 2190 20

Non-10 m bands were resampled to 10 m with bilinear interpolation. (B10 cirrus is not part of the L2A product, so it is not included.)

Splits

splits.json provides a fixed 80/10/10 train/val/test split that is stratified by class and grouped by source Sentinel-2 scene (sklearn.model_selection.StratifiedGroupKFold(n_splits=10) with scene_id as the group, seed 42; fold 0 = test, fold 1 = val, folds 2–9 = train). No scene contributes patches to more than one split, so a model cannot match a test patch to a visually near-identical neighbour from the same scene seen during training. Please use this split when reporting results.

Class Total Train Val Test
Shrubland 5,927 4,742 593 592
Tree cover 5,000 4,000 500 500
Grassland 4,820 3,856 482 482
Cropland 3,854 3,083 385 386
Herbaceous wetland 3,536 2,829 353 354
Permanent water 2,637 2,109 264 264
Bare/sparse veg. 2,410 1,928 241 241
Built-up 1,061 849 106 106
Mangroves 1,017 813 102 102
Moss and lichen 665 532 67 66
Total 30,927 24,741 3,093 3,093

The file maps each split to {class_name: [patch_id, ...]} and also stores class_to_idx and inverse-frequency class weights (clipped at 10.0) for weighted cross-entropy.

Evaluation groupings (eval/)

Two extra artifacts under eval/ make the dataset's similar-but-different structure directly testable. Both are built only from the test split, from the patches' visual-RGB statistics, so a model trained on train has never seen them — no need to retrain to use them. They ask a sharper question than plain per-patch accuracy: when two (or more) patches look alike in RGB but carry different labels, does the model tell them apart?

eval/test_pairs.parquet — 46 pairs of test patches that are close in visual RGB (mean L2 ≤ 2.0 and per-channel std L2 ≤ 3.0) yet differ by a large near-infrared margin (|ΔB08 mean| > 500 SR units). Columns: patch_a, patch_b, label_a, label_b, rgb_l2, std_l2, nir_mean_diff, re_mean_diff. The similar-but-different pairs are the cross-label ones (label_a != label_b, 70% of rows). Pair accuracy = fraction of pairs where the model classifies both endpoints correctly.

eval/test_hard_clusters.parquet — 53 hard clusters (121 patches, long format: one row per membership). Clusters are the connected components of the test-set RGB mean+std similarity graph (same thresholds) that contain ≥ 2 patches spanning ≥ 2 distinct labels — groups that look alike in RGB but cross class boundaries. Columns: cluster_id, patch_id, wc_mode_label, cluster_size, n_labels (sizes: 42×2, 7×3, 4×4). Cluster accuracy = fraction of clusters where the model classifies all members correctly (the size-2 case reduces to pair accuracy).

import pandas as pd
# pred: dict mapping patch_id -> predicted class label (string)

pairs = pd.read_parquet(f"{local}/eval/test_pairs.parquet")
both_correct = (pairs.patch_a.map(pred).eq(pairs.label_a) &
                pairs.patch_b.map(pred).eq(pairs.label_b))
pair_accuracy = both_correct.mean()

clusters = pd.read_parquet(f"{local}/eval/test_hard_clusters.parquet")
ok = clusters.assign(hit=clusters.patch_id.map(pred).eq(clusters.wc_mode_label))
cluster_accuracy = ok.groupby("cluster_id").hit.all().mean()

Reference — a random forest on per-band mean+std (fit on train, the same baseline as below) scores:

Bands Pair accuracy Cluster accuracy
RGB 28% 6%
RGB + NIR 57% 28%
All 12 bands 70% 43%

RGB-only statistics can barely resolve these groups; the non-visible bands are what make them separable — which is the whole point of the dataset.

Quick start

import io, json
import pandas as pd
import rasterio
from huggingface_hub import snapshot_download

local = snapshot_download(repo_id="calebrob6/similar-but-different",
                          repo_type="dataset")

# Read one patch from a shard:
shard = pd.read_parquet(f"{local}/shards/Tree_cover.parquet")
row = shard.iloc[0]
with rasterio.open(io.BytesIO(row["tif"])) as src:
    arr = src.read()              # (12, 32, 32) uint16 surface reflectance
    print(src.descriptions[7])    # 'B08 NIR 842nm'
    print(src.tags())             # {'patch_id': ..., 'wc_mode_label': ...}

# Use the fixed scene-disjoint split:
splits = json.loads(open(f"{local}/splits.json").read())
train_ids = {pid for ids in splits["train"].values() for pid in ids}
train_rows = shard[shard["patch_id"].isin(train_ids)]

Or with the HF datasets library:

from datasets import load_dataset
ds = load_dataset("calebrob6/similar-but-different",
                  data_files="shards/*.parquet")

Baseline results

ResNet-18 (ImageNet init, input conv adapted to the channel count; AdamW + cosine schedule, 50 epochs, batch 256, flips/rotations; reflectance / 10,000). Best run per band set from a sweep over learning rate {3e-4, 1e-3, 3e-3} × class weighting {none, inverse}, on the fixed split above:

Bands used Channels Test accuracy Macro F1 Weighted F1
RGB (B04, B03, B02) 3 0.712 0.727 0.712
RGB + NIR (+ B08) 4 0.770 0.787 0.769
All 12 bands 12 0.822 0.841 0.821

The ordering RGB < RGB+NIR < All holds in every cell of the sweep, and re-running the winning configurations with a different random seed gives 0.717 / 0.772 / 0.817. Frozen foundation-model probes (KNN-5 and linear, in the style of torchgeo-bench) show the same pattern — band-flexible models such as DOFA, Panopticon, and OlmoEarth gain 6–24 points from RGB to the full stack, with an OlmoEarth-v1-Base linear probe reaching 0.867 — see the announcement post for the full table.

Note that the dataset is a controlled probe, not a representative sample of the land surface: class priors and geography reflect the selection procedure, and labels inherit WorldCover's errors (patches are ≥ 70% a single class, but residual label noise remains). Read accuracies as measurements of band reliance, not as operational land-cover accuracy.

License

Released under CC BY 4.0, matching the upstream Sentinel-2 L2A data (Copernicus open access) and ESA WorldCover (CC BY 4.0).

Attribution: Contains modified Copernicus Sentinel-2 L2A data (2024–2025); land-cover labels derived from © ESA WorldCover 2021 v200.

Citation

@misc{similar-but-different-2026,
  title  = {Similar But Different: a Sentinel-2 benchmark for probing
            spectral-band reliance in land-cover models},
  author = {Robinson, Caleb},
  year   = {2026},
  url    = {https://huggingface.co/datasets/calebrob6/similar-but-different}
}
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