Table 1:
Sampling sites from both Missouri and eastern Kansas in 2021 and Indiana in 2022
| State | City | Cultivar | Nematicides Previously Applied | Construction | pH | OM % | K (ppm) | Mg (ppm) | Ca (ppm) |
|---|---|---|---|---|---|---|---|---|---|
| MO/KC 2021 | |||||||||
| 1 | St. Louis | A4 | None | USGA | 6.9 | 1.3 | 40 | 82 | 471 |
| 2 | St. Louis | T1/A4 | None | USGA | N.A. | N.A. | N.A. | N.A. | N.A. |
| 3 | St. Louis | A1/A4 | Heat-killed Burkholderia spp., Fluopyram | Native | N.A. | N.A. | N.A. | N.A. | N.A. |
| 4 | Columbia | A1 | None | USGA | N.A. | N.A. | N.A. | N.A. | N.A. |
| 5 | Columbia | SR 1020 | Heat-killed Burkholderia spp., Abamectin | USGA | 7.8 | 0.6 | 49 | 126 | 634 |
| 6 | Branson | Penn A1/A4 | None | USGA | N.A. | N.A. | N.A. | N.A. | N.A. |
| 7 | Cape Girardeau | Crenshaw | Fluopyram | USGA | N.A. | N.A. | N.A. | N.A. | N.A. |
| 8 | Mission Hills | A1/A4 | Fluopyram | USGA | 7.3 | 1.4 | 30 | 72 | 628 |
| 9 | Mission Hills |
| Heat-killed Burkholderia spp., Abamectin | USGA | 7.1 | 1.2 | 64 | 65 | 597 |
| 10 | Olathe | A4/Pure Distinction | Abamectin, Fluopyram | USGA | 7.2 | 1.3 | 53 | 62 | 678 |
| Indiana 2022 | |||||||||
| 1 | Newburgh | Cohansey | None | USGA | 7.4 | 1.1 | 20 | 51 | 476 |
| 2 | French Lick | Penn A1/A4 | None | USGA | 7.9 | 1.0 | 16 | 35 | 1335 |
| 3 | Columbus | Penncross | Abamectin | Native | 7.5 | 1.6 | 59 | 93 | 1373 |
| 4 | Indianapolis | Penncross ~20% Poa | None | USGA | 7.5 | 2.5 | 49 | 113 | 1478 |
| 5 | Noblesville | A1 | None | USGA | 7.8 | N.A. | N.A. | N.A. | N.A. |
| 6 | Chesterton | Penncross/Poa (50/50) | None | USGA | 7.8 | 1.2 | 21 | 77 | 890 |
| 7 | Bristol | A1/A4/Poa | Fluopyram | Native | 7.8 | 2.2 | 108 | 105 | 1809 |
| 8 | Fort Wayne | Penncross/Poa | None | USGA | 7.6 | 2.6 | 56 | 84 | 1609 |
| 9 | Fort Wayne | 007 | None | USGA | 7.5 | 1.6 | 40 | 138 | 1546 |
| 10 | West Lafayette | L 39 | None | USGA | 7.9 | 1.7 | 30 | 80 | 1518 |
Table 2:
Species and isolates of lance nematodes sequenced in the present study.
| DNA ID | Location | Host | Cultivar | Species | GenBank Accession Number |
|---|---|---|---|---|---|
| STL.1 | Kirkwood, MO | Bentgrass | A1/A4 | H. stephanus | OR948481 |
| STL.2 | Kirkwood, MO | Bentgrass | A1/A4 | H. magnistylus | OR948484 |
| STL.3 | Kirkwood, MO | Bentgrass | A1/A4 | H. stephanus | OR948486 |
| STL.4 | Kirkwood, MO | Bentgrass | A1/A4 | H. stephanus | OR948495 |
| STL.5 | Kirkwood, MO | Bentgrass | A1/A4 | H. stephanus | OR948498 |
| STL.6 | Kirkwood, MO | Bentgrass | A1/A4 | H. magnistylus | OR948501 |
| 1.1 | Newburgh, IN | Bentgrass | Cohansey | H. magnistylus | OR948481 |
| 1.2 | Newburgh, IN | Bentgrass | Cohansey | H. magnistylus | OR948496 |
| 2.1 | French Lick, IN | Bentgrass | Penn A1/A4 | H. stephanus | OR948472 |
| 2.2 | French Lick, IN | Bentgrass | Penn A1/A4 | H. stephanus | OR948480 |
| 2.3 | French Lick, IN | Bentgrass | Penn A1/A4 | H. stephanus | OR948482 |
| 2.4 | French Lick, IN | Bentgrass | Penn A1/A4 | H. stephanus | OR948500 |
| 3.1 | Columbus, IN | Bentgrass | Penncross | H. stephanus | OR948478 |
| 3.2 | Columbus, IN | Bentgrass | Penncross | H. stephanus | OR948493 |
| 3.3 | Columbus, IN | Bentgrass | Penncross | H. stephanus | OR948492 |
| 4.1 | Indianapolis, IN | Bentgrass/~20% Poa | Penncross | H. stephanus | OR948475 |
| 4.2 | Indianapolis, IN | Bentgrass/~20% Poa | Penncross | H. stephanus | OR948485 |
| 5.1 | Noblesville, IN | Bentgrass | A1 | H. stephanus | OR948476 |
| 6.1 | Chesterton, IN | Bentgrass/Poa 50/50 | Penncross | H. stephanus | OR948477 |
| 6.2 | Chesterton, IN | Bentgrass/Poa 50/50 | Penncross | H. stephanus | OR948487 |
| 7.1 | Bristol, IN | Bentgrass/~20% Poa | A1/A4 | H. stephanus | OR948497 |
| 10.1 | West Lafayette, IN | Bentgrass | L 93 | H. stephanus | OR948473 |
| 10.2 | West Lafayette, IN | Bentgrass | L 93 | H. stephanus | OR948474 |
| 10.3 | West Lafayette, IN | Bentgrass | L 93 | H. stephanus | OR948479 |
| 10.4 | West Lafayette, IN | Bentgrass | L 93 | H. stephanus | OR948483 |
| 10.5 | West Lafayette, IN | Bentgrass | L 93 | H. stephanus | OR948489 |
| 10.6 | West Lafayette, IN | Bentgrass | L 93 | H. stephanus | OR948490 |
| 10.7 | West Lafayette, IN | Bentgrass | L 93 | H. stephanus | OR948491 |
| 10.8 | West Lafayette, IN | Bentgrass | L 93 | H. stephanus | OR948494 |
| 10.9 | West Lafayette, IN | Bentgrass | L 93 | H. stephanus | OR948499 |
| 10.10 | West Lafayette, IN | Bentgrass | L 93 | H. magnistylus | OR948502 |
| Root-Knot | |||||
| DNA ID | Location | Host | Cultivar | Species | GenBank Accession Number |
| 1.1 | Newburgh, IN | Bentgrass | Cohansey | M. gramincola | PP034063 |
| 2.1 | French Lick, IN | Bentgrass | Penn A1/A4 | M. gramincola | PP034062 |
| 4.1 | Indianapolis, IN | Bentgrass/~20% Poa | Penncross | M. marylandi | PP034064 |
| 4.2 | Indianapolis, IN | Bentgrass/~20% Poa | Penncross | M. naasi | PP034066 |
| 5.1 | Noblesville, IN | Bentgrass | A1 | M. graminicola | PP034061 |
| 6.1 | Chesterton, IN | Bentgrass/Poa 50/50 | Penncross | M. marylandi | PP034071 |
| 7.1 | Bristol, IN | Bentgrass/~20% Poa | A1/A4 | M. marylandi | PP034065 |
| 7.2 | Bristol, IN | Bentgrass/~20% Poa | A1/A4 | M. naasi | PP034072 |
| 8.1 | Fort Wayne, IN | Bentgrass/Poa 50/50 | Penncross | M. naasi | PP034067 |
| 9.1 | Fort Wayne, IN | Bentgrass | 007 | M. naasi | PP034069 |
| 10.1 | West Lafayette, IN | Bentgrass | L 93 | M. graminicola | PP034060 |
| 10.2 | West Lafayette, IN | Bentgrass | L 93 | M. naasi | PP034068 |
| 10.3 | West Lafayette, IN | Bentgrass | L 93 | M. naasi | PP034070 |
Table 3:
Hoplolaimus spp. reverse primers paired with Hoc-1f (1,19). Meloidogyne spp. primer pairs used in this study (36). All Tm (°C) fell between 55–65.
| Hoplolaimus spp. | |||||
|---|---|---|---|---|---|
| Species | Primer Code | Primer Sequence (5′-3′) | Tm (°C) | Size of PCR fragment (bp) | |
| Hoplolaimus spp. | LSUD-03r | TATGCTTAAGTTCAGCGGGT | 60 | 1,030 | |
| H. stephanus | Hs-1r | GCCAGTGTGTTCCGCTCGCA | 63.2 | 260 | |
| H. stephanus | Hs-1f | CCTGCCTTGGGGGTCGCTTG | 63.7 | 260 | |
| H. columbus | HC-1r | TCAGCACACAATGGTACCTTT | 62 | 580 | |
| H. galeatus | HG-2r | TCCTCGTTCACACATTGACA | 62 | 120 | |
| Meloidogyne spp. | |||||
| Meloidogyne spp.(F) | RK28SF | CGGATAGAGTCGGCGTATC | 55–60 | 612 | |
| Meloidogyne spp.(R) | MR | AACCGCTTCGGACTTCCACCAG | |||
| M. graminis(F) | Mg28SFs | GATGTGCAGATATTTTCCGTCAAGG | 55–60 | 198 | |
| M. graminis(R)* | RK28SUR | CCCTATACCCAAGTCAGACGAT | |||
| M. marylandi(F) | MgmITSFs | GATCGTAAGACTTAATGAGCC | 55–60 | 323 | |
| M. marylandi(R)* | RK28SUR | CCCTATACCCAAGTCAGACGAT | |||
| M. naasi(F) | Mn28SFs | GTCTGATGTGCGACCTTTCACTAT | 55–60 | 272 | |
| M. naasi(R)* | RK28SUR | CCCTATACCCAAGTCAGACGAT | |||
| M. incognita(F) | Inc-K14-F | CCCGCTACACCCTCAACTTC | 55–60 | 399 | |
| M. incognita(R) | Inc-K14-R | GGGATGTGTAAATGCTCCTG | |||

Figure 1:
Distribution of plant-parasitic nematode species sampled from creeping bentgrass putting greens in Missouri and eastern Kansas in 2021 and Indiana in 2022 in two independent pie charts. Samples were collected during the months of April, June, August and October of 2021 and 2022, respectively. “n” indicates total PPNs represented within each chart.
Table 4:
Type III Tests of Fixed Effects for both Missouri and eastern Kansas in 2021 and Indiana in 2022. Data were analyzed using PROC GLIMMIX in SAS 9.4
| Effect | Missouri | Indiana | |
|---|---|---|---|
| Lance | Depth | <.0001 | <.0001 |
| Month | .0028 | .0003 | |
| Depth x Month | .0487 | .4981 | |
| Root-Knot | Depth | .0004 | <.0001 |
| Month | .7918 | <.0001 | |
| Depth x Month | .9998 | .5897 | |
| Ring | Depth | <.0001 | <.0001 |
| Month | <.0001 | <.0001 | |
| Depth x Month | .0001 | <.0001 | |
| Free-Living | Depth | <.0001 | <.0001 |
| Month | .0538 | .0025 | |
| Depth x Month | .0254 | <.0001 |
Table 5:
Missouri and eastern Kansas 2021 total nematode population densities by sampling depth and month with soil samples aggregated (100 cm3). Significance letters indicate significant differences between sampling depths by month analyzed within that individual species.
| Sampling Depth (cm) | |||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| Species | Sampling Month | 0–5 | 5.1–10 | 10.1–15 | 15.1–20 | 20.1–25 | |||||
| Lance | April | 81.9x | bcdey | 19.5 | de | 9.0 | e | 1.5 | e | 1.5 | e |
| June | 144.0 | b | 85.5 | bcde | 18.0 | e | 10.5 | e | 10.5 | e | |
| August | 147.6 | b | 110.7 | bc | 53.1 | cde | 33.6 | cde | 21.3 | cde | |
| October | 309.0 | a | 105.6 | bcd | 27.0 | cde | 24.9 | cde | 10.8 | e | |
| Root-Knot | April | 162.9 | * | 66.0 | * | 14.4 | * | 12.0 | * | 3.0 | * |
| June | 97.5 | * | 39.0 | * | 4.5 | * | 3.0 | * | 13.5 | * | |
| August | 114.6 | * | 25.5 | * | 5.1 | * | 4.5 | * | 9.0 | * | |
| October | 185.4 | * | 62.1 | * | 11.4 | * | 8.1 | * | 15.9 | * | |
| Ring | April | 21.9 | c | 27.0 | c | 21.0 | c | 3.0 | c | 3.9 | c |
| June | 90.0 | cb | 64.5 | cb | 34.5 | cb | 13.5 | c | 18.0 | c | |
| August | 171.3 | b | 97.5 | cb | 37.2 | cb | 17.7 | c | 23.1 | cb | |
| October | 534.0 | a | 139.5 | cb | 62.7 | cb | 33.6 | cb | 18.3 | cb | |
| Free-Living | April | 1188.9 | c | 238.5 | c | 80.4 | c | 43.8 | c | 43.8 | c |
| June | 3178.5 | b | 429.0 | c | 189.0 | c | 114.0 | c | 90.0 | c | |
| August | 3187.2 | b | 306.7 | c | 154.2 | c | 108.3 | c | 143.1 | c | |
| October | 4653.0 | a | 351.8 | c | 186.9 | c | 100.5 | c | 119.8 | c | |
Table 6:
Indiana 2022 total nematode population densities organized by sampling depth and month with soil samples aggregated (100 cm3). Significance letters indicate significant differences between sampling depths by month analyzed within that individual species.
| Sampling Depth (cm) | |||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| Species | Sampling Month | 0–5 | 5.1–10 | 10.1–15 | 15.1–20 | 20.1–25 | |||||
| Lance | April | 30.0x | *y | 37.5 | * | 16.5 | * | 18.0 | * | 4.5 | * |
| June | 16.5 | * | 63.0 | * | 13.5 | * | 4.5 | * | 3.0 | * | |
| August | 51.0 | * | 54.0 | * | 43.5 | * | 34.5 | * | 15.0 | * | |
| October | 10.5 | * | 19.5 | * | 16.5 | * | 6.0 | * | 4.5 | * | |
| Root-Knot | April | 424.5 | * | 306.0 | * | 229.5 | * | 79.5 | * | 48.0 | * |
| June | 145.5 | * | 67.5 | * | 19.5 | * | 4.5 | * | 0 | * | |
| August | 282.0 | * | 132.0 | * | 28.5 | * | 27.0 | * | 22.5 | * | |
| October | 70.5 | * | 55.5 | * | 18.0 | * | 9 | * | 7.5 | * | |
| Ring | April | 189.0 | bcd | 58.5 | cde | 21.0 | de | 19.5 | de | 16.5 | e |
| June | 337.5 | b | 153.0 | cde | 57.0 | de | 30.0 | de | 19.5 | de | |
| August | 1017.9 | a | 220.5 | bc | 121.5 | cde | 61.5 | cde | 33.0 | de | |
| October | 156.0 | cde | 57.0 | cde | 33.0 | de | 13.5 | e | 1.5 | e | |
| Free-Living | April | 1591.5 | b | 316.5 | c | 129.0 | c | 73.5 | c | 58.5 | c |
| June | 4144.5 | a | 405.0 | c | 132.0 | c | 60.0 | c | 28.5 | c | |
| August | 3559.5 | a | 343.5 | c | 160.5 | c | 61.5 | c | 60.0 | c | |
| October | 913.5 | bc | 147.0 | c | 67.5 | c | 43.5 | c | 30.5 | c | |

Figure 2:
Phylogeny of the rDNA ITS region of Hoplolaimus spp. isolated from golf putting greens. Phylogenetic trees were constructed with the neighbor-joining algorithm using the Kimura two-parameter model with Litylenchus spp. (LC383724) as the outgroup. Bootstrap values are based on 1000 resamplings of the data set. DNAID codes correlate to Table 2.

Figure 3:
PCR results using Hoplolaimus-specific and H. stephanus, H. columbus and H. galeatus-specific primers. DL: DNA Ladder; 1: Hoplolaimus spp. (DNA ID:10); 2: H. stephanus (DNA ID:10); 3: H. columbus (DNA ID:10); 4 H. galeatus (DNA ID:10); 5: Hoplolaimus spp. (DNA ID:3); 6: H. stephanus (DNA ID:3); 7: H. columbus (DNA ID:3); 8 H. galeatus (DNA ID:3); 9: Hoplolaimus spp. (DNA ID:4); 10: H. stephanus (DNA ID:4); 11: H. columbus (DNA ID:4); and 12 H. galeatus (DNA ID:4).

Figure 4:
Scanning-electron micrographs of a lance nematode specimen collected form Site 5. A) four lip annules; B) the presence of an epiptygma; C) 25 longitudinal striae on the basal lip annule; and D) four lateral incisures.

Figure 5:
Phylogeny of molecularly characterized Meloidogyne spp. isolated from golf coursed based on D2/D3 28S genes. phylogenetic trees were constructed with the neighbor-joining algorithm using the Kimura two-parameter model with Litylenchus spp. (LC383724) as the outgroup. Bootstrap values are based on 1000 resamplings of the data set and displayed near branch nodes. DNAID codes correlate to Table 2.

Figure 6:
PCR results using Meloidogyne-specific and M. naasi and M. marylandi-specific primers. DL: DNA Ladder; 1: Meloidogyne spp. (DNA ID:9); 2: M. naasi (DNA ID:9); 3: Meloidogyne spp. (DNA ID:4); 4: M. marylandi (DNA ID:4); and 5: Meloidogyne spp.(DNA ID:4).